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Funding Provided by: Southern Nevada Public Lands Management Act
Bureau of Land Management
Natural Resources Conservation Service
Prepared by: Tahoe Resource Conservation District
870 Emerald Bay Rd. Suite 108
South Lake Tahoe, CA 96150
(530) 543-1501
TahoeRCD.org
Prepared for: Natural Resources Conservation Service
District Conservationist 870 Emerald Bay Road
South Lake Tahoe, CA 96150
Submitted: February 26, 2014
Community Watershed Partnership
Introduction………………………………………..…………………………………................. 1
Description of the Area…………………………………………………………………............. 4
Goals………………………………………………………………............................................. 10
Stakeholder and Community Outreach…................................................................................ 10
Community Forums and Workshops………………………………………………............... 14
Activities………………………..……………………………………………….……………… 17
Landscape Conservation………………………………………………….............................. 17
Results……………………………………………………………………………………...…... 22
Private Parcel Technical Assistance…………….…………………………………............... 22
BMP Assistance…………………………………………………………………................... 22
Community Science and Stewardship Activities……………………………….................... 24
Project Partners and Stakeholders………….…………………………………....................... 31
Lessons Learned……………………………………………………………………………….. 32
Appendix A…………………….Community Watershed Partnership Outreach Brochure and Flier
Appendix B…………………………………...Community Watershed Partnership Survey Results
Appendix C, D……”Omitted for Privacy”….........................Technical Services Summary Tables
Appendix E………………………………………………………...Wet Soils BMP Plan Template
Appendix F…………...……………………………………..Soil Infiltration Investigation Report
Appendix G………………...….……………………………….Streamkeepers Monitoring Report
Appendix H………”Omitted for Privacy”…………Invasive Weeds Mapping and Removal Data
Figure 1.………………………………………..Community Watershed Partnership Ranking Map
Figure 2…………………………….……..South Lake Tahoe CWP and Associated Communities
Figure 3…………………………………………Kings Beach CWP and Associated Communities
Figure 4……………………………………….CWP Environmental Priorities, South Lake Tahoe
Figure 5……………………………………….…….CWP Environmental Priorities, Kings Beach
Figure 6……………………………………………….CWP Stewardship Activities by Preference
Figure 7…………………………………………………...Summary Table of Project Deliverables
Figure 8…………………………………………………2012 Streamkeepers Monitoring Reaches
Figure 9…………………………...2013 Snapshot Day Monitoring Sites in the Lake Tahoe Basin
Figure 10……………..…….2012 Tahoe Resource Conservation District Invasive Plant Mapping
Table of Contents
Figures
Appendices
BMP…………………………………………………………………...Best Management Practices
CWP…………………………………………………………..Community Watershed Partnership
EIP…………………………………………………………Environmental Improvement Program
NRCS……………………………………………………..Natural Resource Conservation Service
NTCD………………………………………………………..Nevada Tahoe Conservation District
SNPLMA……………………………………….Southern Nevada Public Lands Management Act
TMDL………………………………………………………………...Total Maximum Daily Load
Tahoe RCD…………………………...……………………Tahoe Resource Conservation District
TRPA…………………………………………………………...Tahoe Regional Planning Agency
UNCE……………………………………………….University of Nevada Cooperative Extension
Acronyms
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March 2014 – NRCS FINAL REPORT Community Watershed Partnership Tahoe Resource Conservation District
Introduction
The clear waters of Lake Tahoe have earned the title “Jewel of the Sierras.” Each year millions of
visitors travel to Lake Tahoe to experience its beauty and take advantage of the myriad of
opportunities for recreation and tourism. Unfortunately increased development and urban
infrastructure has resulted in the loss of natural pollutant filtering mechanisms throughout the
watershed, while at the same time impervious surfaces generate a larger number of pollutants
within urban areas.
In order to assist with pollutant load reductions the Community Watershed Partnership (CWP)
Program supports implementation of the Basin’s Environmental Improvement Program (EIP), a
cooperative public/private effort to preserve, restore and enhance the environment of the Lake
Tahoe Region. As required by the Tahoe Regional Planning Agency (TRPA), all private property
owners are required to install best management practices (BMPs) that reduce pollutants entering
Lake Tahoe. The Total Maximum Daily Load (TMDL) is another mechanism for implementing the
EIP program and it requires all storm water jurisdictions in the Basin to decrease pollutant
loading from urban runoff as well.
The focus on capturing and treating stormwater has become a priority since the Lake Tahoe TMDL
identified that approximately 72 percent of the primary pollutants entering Lake Tahoe come
from urban runoff. The Lake Tahoe EIP has established a process for implementing restoration
projects, and has provided millions of dollars through the Southern Nevada Public Lands
Management Act (SNPLMA) for implementation of pollutant control projects.
Through the development of the CWP Program the Tahoe Resource Conservation District (Tahoe
RCD), the Nevada Tahoe Conservation District (NTCD), and the Natural Resources Conservation
Services (NRCS) have provided extensive technical assistance and education to private property
owners in order to contribute to the reduction of pollutants that effect Lake Tahoe’s unique clarity,
beauty and bountiful natural resources for future generations.
After a decade of implementing the BMP program, efficiencies were needed and new community
engagement opportunities were identified through stewardship and landscape conservation
practices. This led to a more flexible and inclusive program dedicated to finding alternate ways to
implementing BMPs. Simultaneously, the Lake Tahoe TMDL was adopted and there was a growing
consensus that Tahoe Basin programs needed to improve effectiveness while finding efficiencies.
Ultimately the growing desire to integrate multiple resource objectives led to the development of
the Community Watershed Partnership.
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March 2014 – NRCS FINAL REPORT Community Watershed Partnership Tahoe Resource Conservation District
The CWP program has been developed within the Tahoe Basin through funding provided by the
Southern Nevada Public Lands Management Act (SNPLMA). The funding for this program is intended
to identify and address natural resource concerns at the sub-watershed level in the Tahoe Basin. The
Tahoe RCD, NRCS, and NTCD are the lead project proponents within this program, however, reliance
on input from additional stakeholders including local jurisdictions, state and federal agencies, local
residents and community members are considered an imperative and integral component in moving
this program forward in a successful manner.
The CWP approach also acknowledges, while many of the environmental improvement projects being
implemented around the Tahoe Basin are being conducted by agencies like the U.S. Forest Service or
local jurisdictions, each person or homeowner also has an opportunity to become an environmental
steward and to contribute to ongoing restoration efforts within their community. The CWP process
aims to educate the public and to facilitate communication among environmental agency stakeholders
and community members and residents.
In 2002 the Tahoe RCD, NTCD, NRCS, and TRPA adopted a Memorandum of Understanding to
establish a partnership that would provide technical support to homeowners, contractors and
property managers in implementing water quality BMPs. Through grant funded incentive
programs, the Tahoe RCD and its partners provided cost free property evaluations and BMP
implementation plans. The deadline for implementing BMPs was established by the TRPA
accompanied by a penalty fee in order to stimulate requests for BMP services. The deadline for
Basin-wide implementation, was slated for 2008, this date has since come and gone with little
regulatory response. Additional program challenges include public perception and cost; BMP
implementation is perceived as burdensome by many property owners, and education and
outreach efforts have not been as effective as projected.
After more than a decade, in 2013, approximately three out of every ten private properties in the
Tahoe Basin had achieved BMP compliance. In order to accelerate implementation the TRPA has
recently begun enforcement activity. This action has resulted in increased implementation in
targeted areas. Beyond regulatory action, the Tahoe RCD has continued to provide technical
assistance, outreach and education such that private property owners better understand the
connection between their land use practices and water quality. This approach also now
incorporates opportunities to engage residents in stewardship activities.
In order to better contribute to the larger scale planning efforts in the Basin, the Tahoe RCD
reached out to community members with information to help guide their actions related to
general landscape management such as native and fire-wise plant care and erosion control
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March 2014 – NRCS FINAL REPORT Community Watershed Partnership Tahoe Resource Conservation District
management. This landscape conservation approach included BMP technical assistance but took a
holistic approach to tackling natural resource concerns while providing quality of life benefits.
This modified approach resulted in a greater enthusiasm within a new audience; new or novice
gardeners began searching out technical assistance. The Landscape Conservation approach
provided the Tahoe RCD a new opportunity to re-engage the public and offer site specific, in-
person consultations to address homeowner questions and challenges. In fact, after the Angora
Fire of 2006, service requests for landscape consultations boomed as homeowners looked for
assistance to revegetate and stabilize their property after the construction of their new homes in
the burn area. Both the TRPA and the local jurisdictions began to refer homeowner landscaping
questions to the Tahoe RCD. The South Tahoe Public Utility District’s Turf Buyback Program and
the Tahoe RCD’s Native Plant Start-up Kit further incentivized soil restoration and revegetation
projects.
Today, the Tahoe RCD utilizes the landscape conservation approach within the CWP program to
reach the hearts and minds of the Tahoe Basin residents.
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March 2014 – NRCS FINAL REPORT Community Watershed Partnership Tahoe Resource Conservation District
Description of the Area
As part of developing the CWP process it became important to identify selection criteria to help
focus the project team on priority watershed catchments. Selection of the targeted sub-watershed
area and subsequent areas of Community Watershed Partnership were based on the following
criteria:
pollutant loading, wildfire risk, and presence of invasive species
areas identified as high priority by agency representatives and resource managers
collaboration and agreement of selected watershed area amongst agency representatives
environmental improvement project implementation
existing natural resource issues or low BMP compliance
expected community participation and enthusiasm
The CWP ranking map shown on the following page (Figure 1) identifies priority CWP areas in
Lake Tahoe as created by NRCS partners. Those sub-watersheds shown in Red represent the high
priority areas. Not surprisingly these areas also commonly represent dense urban cover. Sub-
watersheds shown in orange and yellow tend to represent either mixed use or less populated
areas; green sub-watershed areas indicate the low priority sites typically upland forested areas
with low population densities.
The target CWP areas identified for this work were South Lake Tahoe HWY 50 corridor and Kings
Beach, California. Not only are they densely populated, with extensive impervious surface and
erosion hazards, but they are both considered to have disadvantaged communities. In support of
the EIP, responsible storm water jurisdictions have implemented a long list of capital
improvements to storm water infrastructure. The project list may be viewed at
http://tahoercd.org/tahoe-community-watershed-planning/.
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March 2014 – NRCS FINAL REPORT Community Watershed Partnership Tahoe Resource Conservation District
Figure 1: CWP Watershed Ranking
Com m un it y Wat ershed Par t nersh ip
Pr io r it y Ranking
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March 2014 – NRCS FINAL REPORT Community Watershed Partnership Tahoe Resource Conservation District
South Lake Tahoe
The South Lake Tahoe CWP focus area covers 5.2 square miles in the communities of Al Tahoe,
Sierra Tract, and portions of the “Y” area and the Tahoe Keys (Figure 2). This CWP area includes
neighborhoods which lie in close proximity to the lake as well as two primary tributaries, the
Upper Truckee River (UTR) and Trout Creek which intersect in the Upper Truckee Marsh before
entering Lake Tahoe. The CWP focus area within the Upper Truckee River and Trout Creek
Watersheds is located in the uppermost urbanized reaches of the watersheds. The Upper Truckee
River sub-watershed is located along the southern end of the Lake Tahoe Basin, and lies within the
City of South Lake Tahoe and El Dorado County. At 56.6 square miles, the Upper Truckee River is
the largest watershed in the Lake Tahoe Basin; TMDL research also identified this tributary as the
greatest contributor of nutrients and sediment as compared with all other tributaries in the Tahoe
Basin.
The main channel of the Upper Truckee River (UTR) is 21.4 miles long and originates in the
volcanic bluffs surrounding Meiss Meadow near Carson Pass. The river then flows northward
through a series of meadows and lakes until it reaches an 800-foot glacial step over, where it
enters the head of Christmas Valley. The river flows through Christmas Valley until is it met by
Angora Creek, downstream of the present-day Lake Tahoe Golf Course (LTGC). The UTR continues
to flow northward through Sunset Ranch, the Lake Tahoe Airport, and to the eastern side of the
Tahoe Keys through Cove East where it drains to Lake Tahoe.
The Trout Creek Watershed is the second largest watershed in the Lake Tahoe Basin (it occupies
13 percent of the total land area draining to Lake Tahoe) and is located within the City of South
Lake Tahoe and El Dorado County. The area of the watershed is 41.3 square miles and contains
several second order streams including Saxton Creek, Cold Creek, and Heavenly Valley Creek.
Although Euro-American presence in the Upper Truckee and Trout Creek watersheds created a
myriad of relic resource issues related to heavy logging and cattle grazing; more recent impacts
(within the last 50 to 60 years) associated with concentrated urban development and recreational
activities.
Today, restoration of degraded environmental conditions is paramount in these two watersheds.
Much of the efforts have focused on re-connecting stream channels to their historic flood plains as
well as capturing storm water runoff from the central Highway 50 corridor. In addition, fuel-
reduction activities and habitat restoration have also been a major focus of the urban/wild land
interface.
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March 2014 – NRCS FINAL REPORT Community Watershed Partnership Tahoe Resource Conservation District
Figure 2: South Lake CWP and Associated Communities
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March 2014 – NRCS FINAL REPORT Community Watershed Partnership Tahoe Resource Conservation District
Kings Beach
The Kings Beach CWP Area covers 12.5 square miles and includes the residential areas of
Brockway, Kings Beach, and Tahoe Vista (Figure 3). The Kings Beach Watershed is jointly located
in the North Eastern portion of Placer County. It contains the subwatersheds of Kings Beach (2.9
square miles), Griff Creek (4.squarere miles), and Tahoe Vista (1.4 square miles). The total
drainage area of the watershed is 8.8 square miles.
Griff Creek is approximately 6.4 kilometers long with headwaters west of Martis Peak at 8,742 feet
of elevation, and Snow Creek is approximately 5.4 kilometers long with headwaters near
Brockway summit at 7,199 feet elevation. The southern portion of the watershed is dominated by
privately owned residential and commercial properties, whereas the northern portion is primarily
forested area owned and managed by the US Forest Service Lake Tahoe Basin Management Unit.
The Kings Beach area was heavily logged and in the early 1860’s, to supply lumber for the silver
mines in Virginia City, Nevada and the surrounding areas. Restoration activities are focused on
stream and meadow restoration as well as associated impacts related to more recent concentrated
urban development and recreational activities.
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March 2014 – NRCS FINAL REPORT Community Watershed Partnership Tahoe Resource Conservation District
Figure 3: Kings Beach CWP and Associated Communities
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March 2014 – NRCS FINAL REPORT Community Watershed Partnership Tahoe Resource Conservation District
Goals
The goals of Community Watershed Partnership were to interact with the community, discover
the challenges they face in their watershed, and work with them as well as other stakeholders to
come up with solutions. The first step in the process was to interact with the community and
solicit feedback from them.
Stakeholder and Community Outreach
Outreach has been an important aspect of involving the residents of the Tahoe Basin, and more
specifically the CWP areas. Many different strategies were employed to create awareness and
participation in CWP, including:
Direct mail to targeted areas
Local newspaper advertising
Local radio talk shows and advertising
Cable television interviews
Online promotion, including website, interactive blog and social media (Facebook &
Twitter)
Neighborhood canvassing by Tahoe RCD staff
Neighborhood events, including a block party and public forum
Surveys (online, paper form and informal discussions)
Community events
Shared messaging with Lake Tahoe Master Gardeners
The CWP is a new type of conservation initiative in the Tahoe Basin, strategies were employed
based on trial and error and availability of resources, including staff time and programmatic
funding. The CWP outreach brochure and flier is attached in Appendix A. A brief description and
assessment of each of these strategies is included below:
Direct mail to targeted areas
Direct mail can be an effective way to reach targeted residents, but it is also one of the most
costly outreach alternatives. During this reporting period, direct mail from Tahoe RCD was
limited to residences who received a BMP plan based on physical characteristics of their
property.
In addition to direct mail, Tahoe RCD was able to reach CWP target areas through the
contribution of newsletter articles, and bill inserts joint mailers by TRPA. Newsletter
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March 2014 – NRCS FINAL REPORT Community Watershed Partnership Tahoe Resource Conservation District
contributions included: “Tahoe in Depth,” the TRPA quarterly newsletter, regarding
demonstration gardens, and “The Keys Breeze”, on Conservation Landscaping programs
and events, and North Tahoe PUD to promote cost free BMP and Conservation Landscaping
Assistance in the Kings Beach community. Tahoe RCD was able to promote the Sustainable
Landscaping workshops and Conservation Landscaping technical assistance in the South
Tahoe PUD bill insert. Finally, cost free BMP services were offered to selected homeowners
in Al Tahoe Community within a TRPA BMP accelerated implementation certified letter.
Local newspaper advertising
Newspaper advertising proved to be valuable in attracting community members to
neighborhood events. According to surveys and informal contact with the community,
many members of the South Lake Tahoe community get the majority of their news from
local publications, such as the Tahoe Daily Tribune and the Tahoe Mountain News, both of
which were used to advertise community events.
Local radio talk shows and advertising
After performing media research, Tahoe RCD utilized paid and free airtime on KTHO FM
radio; the highest rated serving the Lake Tahoe Basin. Staff also appeared on several
“morning show” programs to explain CWP to the community. Some forum participants
mentioned hearing ads promoting CWP and the forum event.
Cable television interviews
Staff appeared on “Tahoe Today,” a talk television show on Lake Tahoe Television (Outside
TV), available to all cable subscribers in the Lake Tahoe area.
Online promotion, including website, interactive blog and social media
The website “OurTahoeWatershed.org” was launched in the spring, and was updated
continuously throughout the summer, and also promoted on Tahoe RCD social media
outlets, such as Facebook and Twitter. The blog was launched as an interactive way to
respond to forum comments, online users and community concerns. It is fast becoming an
effective way to update the public on ongoing issues, such as cleanup projects, recreation
questions and watershed health issues.
Neighborhood canvassing by Tahoe RCD
In 2013, Tahoe RCD went door to door in the Kings Beach Community offering free BMP
technical assistance including BMP evaluations, BMP final inspections, and landscape
conservation consultations. During this effort, approximately 125 properties were
contacted by leaving a door hanger offering this limited time offer and approximately 20
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March 2014 – NRCS FINAL REPORT Community Watershed Partnership Tahoe Resource Conservation District
residents were present during this effort allowing staff to fully explain the program and
available services. The information on the door hangers was in both English and Spanish to
increase outreach to the large Spanish speaking population that resides within the Tahoe
basin. Approximately 32 properties received BMP evaluations from this effort.
Surveys (online, paper form and informal discussions)
Within CWP target areas, surveys were implemented by Tahoe RCD staff in summer and
early fall of 2012 to gain a greater understanding of community identified issues, to solicit
community feedback and to help with future CWP planning. Residents and second
homeowners of the Tahoe Basin were targeted via CWP neighborhood BBQ events, local
farmers’ markets, and additional partner outreach events throughout the North Shore and
South Shore communities on the California side of the Basin. Surveys were administered
hardcopy, online and via smartphone, with a total of 84 participants. The primary focus of
these surveys is to identify the environmental priorities of Lake Tahoe residents (Figure 4
& 5) while developing a better understanding of our community’s preference of
stewardship activity engagement (Figure 6). The Tahoe RCD is specifically interested in the
public’s level of knowledge and interest in our programs, as well as the level at which
residents will fund and or participate in stewardship events. Survey results also allow the
Tahoe RCD to discern differences between the North, South and West Shore communities.
Complete survey results are included in Appendix B.
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March 2014 – NRCS FINAL REPORT Community Watershed Partnership Tahoe Resource Conservation District
Figure 4: CWP community environmental priorities (South Shore)
Figure 5: CWP community environmental priorities (North Shore)
020406080
100120140160180
Environmental issues of greatest concern to S. Shore participants (weighted score)
0102030405060708090
Environmental issues of greatest concern to N. Shore participants (weighted score)
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March 2014 – NRCS FINAL REPORT Community Watershed Partnership Tahoe Resource Conservation District
Figure 6: CWP community stewardship activities by preference.
Community Events
Through the participation in established and popular community events, Tahoe RCD was
able to conduct outreach in the community with minimal staff commitment and advertising
expense. Tahoe RCD was able to provide outreach materials and answer questions related
to community environmental projects, conservation landscaping and BMP topics at the
following events: Tahoe Truckee and South Shore Earth Day, Autumn Festival, Live at
Lakeview free concert series, Farmers Market, Wildfire Awareness Week, Native Species
Festival, Lake Tahoe Home and Garden Show and Keep Tahoe Blue’s Summer Kick-off. At
these events Tahoe RCD had the opportunity to interact with hundreds of homeowners by
sharing conservation landscaping principles and practices.
Community Forums and Workshops
Based on attendance records, attracting community members to attend neighborhood CWP
forums proved challenging; therefore, the Tahoe RCD started to look at ways that we could
Page 15 |
March 2014 – NRCS FINAL REPORT Community Watershed Partnership Tahoe Resource Conservation District
participate in activities that already had some momentum such as larger public gatherings or
events instead of being the sole host and event coordinator. Over the course of this grant, the
Tahoe RCD began to look for alternate ways to reach the CWP community. A summary of Tahoe
RCD efforts follow:
Community Watershed Partnership Forums: June 27 and June 28, 2012
Tahoe RCD hosted the Upper Truckee
Meadows and the Kings Beach CWP
forums to gain community input regarding
conservation issues with in the target
communities and invite partner agencies
to distribute information on local
environmental projects within these
watershed areas. Approximately 45
people were in attendance at the
combined events. Here interactive
exhibits, presentations and local agency
presence provided educational opportunities, shared project information, addressed
specific EIP questions, and collected community feedback on environmental issues of
interest. Agencies and environmental groups invited to participate in the events included:
California Tahoe Conservancy, City of South Lake Tahoe, Tahoe Regional Planning Agency,
US Forest Service, Explore Tahoe, UC Cooperative Extension, South Tahoe PUD, North
Tahoe PUD, Placer County, North Tahoe FD, Tahoe Environmental Research Center, Sierra
Watershed Education Partnerships, and Truckee Aquatic Invasive Species Program.
Neighborhood Service Team Meeting: April 25, 2013
The Tahoe RCD participated in the Neighborhood Service Team meeting which included
the Al Tahoe community. Thirty-two community members participated in the meeting.
With community input and facilitation provided by the City of South Lake Tahoe,
community members evaluated multiple community project options and selected a BMP
demonstration project. The City of South Lake Tahoe will contribute to the project by
providing community coordination, construction materials, and other support as needed.
The goal is to implement one residential demonstration project with in 2014 through
complementary funding sources.
Shared messaging with UCCE Lake Tahoe Master Gardeners
Tahoe RCD coordinated with Lake Tahoe Master Gardener Volunteers to receive and
respond to landscape related queries including firewise and waterwise landscaping,
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March 2014 – NRCS FINAL REPORT Community Watershed Partnership Tahoe Resource Conservation District
invasive weeds, native plants and erosion control via a question line, email and office hours
at the Tahoe RCD, and regular staffing at public events. The Lake Tahoe Master Gardener
office is located within Tahoe RCD where programmatic materials and supplies are shared
for the sometimes joint implementation of landscape conservation programs, outreach
materials and events. In 2013, through a partnership with the Tahoe RCD, volunteer Lake
Tahoe Master Gardeners reached 1377 community members including: 980 at workshops,
272 at events, 62 via work with school gardens, 63 in other ways (e.g. office visits).
Through this partnership, Tahoe RCD staff was able to provide three-60 minute
presentations as part of the Lake Tahoe Master Gardener Green Thumb Gardening series.
Presentations included BMPs for Single Family Homes and Irrigation Efficiency on August
5th, 12th and 13th in South Lake Tahoe and Tahoe City. The presentations provided
information and resources on the integration of vegetation into BMPs, proper selection of
plant species based upon property site analysis, and water efficient landscaping practices
and technology.
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March 2014 – NRCS FINAL REPORT Community Watershed Partnership Tahoe Resource Conservation District
Activities
Landscape Conservation
Encouraging Lake Tahoe residences to practice stewardship of Lake Tahoe’s natural resources
through participating in Landscape Conservation consultations proved to be an effective outreach
tool for the Tahoe RCD. These consultations provide a unique opportunity for the private property
owners to invite Tahoe RCD staff onto their property in order to discuss conservation issues and
environmental stewardship. As part of this service the Tahoe RCD provided free landscape
supplies of native plants and wildflower seed. Over 300 native plants were issued to homeowners
and for habitat and restoration projects within the Tahoe basin through this program.
Landscape Conservation technical assistance was provided to 208 property owners through this
funding. Here, one-on-one assistance was provided on-site by Master Gardeners trained to
address various problems and questions surrounding integrated landscaping techniques and
practices. These topics included: identifying and managing invasive weeds, restoring compacted
and nutrient poor soil areas for re-establishment of native species, integrating defensible space
with water quality BMPs, slope stabilization, water conservation, sustainable turf care, turf
conversion and forest health. Resources and information was provided during the on-site
consultation and follow-up information was included in a standardized follow-up letter.
Tahoe RCD staff also distributed information and resources on Tahoe specific backyard
conservation topics during site visits, enclosed within BMP plan and technical assistance mailers,
and in person during site visits, office hours, at events and workshops and through the
distribution of Home Landscaping guides at Realtor offices, plant nursery and building supply
retailers.
Distributed resources include:
Tahoe RCD, NRCS Backyard Conservation, University of Nevada Cooperative Extension
(UNCE) fact sheets and publications, and other publications on the topics of natural
resource protection associated with landscaping practices (fertilizer use, water-wise
landscaping, sustainable turf care, landscaping for erosion control, invasive weeds,
defensible space, plants for the Lake Tahoe Basin and approximately 640 Home
Landscaping Guides for the Lake Tahoe Basin and Vicinity).
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March 2014 – NRCS FINAL REPORT Community Watershed Partnership Tahoe Resource Conservation District
Workshops and events include:
Sustainable Landscaping Workshops: June 5, July 16, Aug. 20, and Aug. 27, 2013
Through discussions with private property owners the Tahoe RCD learned that the rising
cost of water is of high concern to community residences; specifically those residents who
now have water consumption meters versus those paying for a flat consumption rate. In
2012, proper yard fertilization and irrigation in the Lake Tahoe Basin was identified as a
priority issue by local agencies to help control pollutant runoff from commercial and
residential properties and a collaborative fertilizer and irrigation working group has been
established to address Basin needs and to share resources, messaging and funding
opportunities.
Through a partnership with South Tahoe
PUD, Tahoe RCD and Lake Tahoe Master
Gardeners organized four Sustainable
Landscaping workshops which served as
forums in the in the 2013 CWP target areas:
South Lake Tahoe HWY 50 corridor and
Kings Beach. These forums were offered in
response to the demand for information on
how to reduce water use in the landscape
while maintaining landscape esthetics,
defensible space and erosion control
measures.
These 2-hour workshops were packed with helpful resources and included easy to apply
information for local homeowners and businesses. The transport of pollutants to Lake
Tahoe through the modification of landscape practices such as irrigation, turf maintenance,
turf conversion, landscape design and fertilizer management was presented by Tahoe RCD,
South Tahoe PUD and Lake Tahoe Master Gardeners. Total workshop attendance was 58
people.
Participants were surveyed to gain an understanding of pre-workshop landscape practices.
The survey results showed that less than 50% of workshops participants had turf and
about 80% of people were in need of information pertaining to fertilizer and irrigation
management. Additionally, approximately 80% of participants showed little knowledge
regarding soil condition and its relationships to healthy landscapes and erosion. Survey
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March 2014 – NRCS FINAL REPORT Community Watershed Partnership Tahoe Resource Conservation District
results also indicated that participants left with a better understanding of proper fertilizer
and irrigation management and how these practices affect pollutant runoff to Lake Tahoe.
Conservation Landscape Tour: August 11, 2013
The 2013 Conservation Landscape Tour was planned in partnership with South Tahoe PUD
and Lake Tahoe Master Gardeners for the Tahoe Keys Community to increase awareness of
sustainable landscaping and gardening practices in the CWP target area. The annual Tour
provides the Tahoe gardener and homeowner inspiration and education for creating water
wise and synthetic fertilizer free landscapes featuring native and Tahoe-adapted plants.
This event specifically featured properties in the Tahoe Keys community that had
undergone turf conversion projects with incentives provided by South Tahoe PUD’s Turf
Buy-Back program and District’s Landscape Conservation consultation services. The Tahoe
Keys community area was highlighted in this tour due to its proximity to the shore zone
and the associated amount of pollutants that enter the Tahoe Keys waterways in the form
of lawn fertilizer.
The self-guided program invited the community to share first hand experiences with the
homeowners and ask questions from resource professionals and volunteers from the
District, South Tahoe PUD, TRPA, Lake Tahoe Master Gardeners and ACE AmeriCorps.
During the tour, event participants were invited to attend 20 minute educational
presentations and enjoy refreshments provided by the Tahoe Keys Property Owners
Association. Presentation titles included: Fertilizing for Green Grass and Tahoe Blue, Tahoe
Keys Aquatic Invasive Species Management Program, Water wise Landscaping, Sprinkler or
Shower - Water Efficient Irrigation, Happy Soil = Happy Plants and Extending the growing
season permaculture style.
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March 2014 – NRCS FINAL REPORT Community Watershed Partnership Tahoe Resource Conservation District
BMP Contractors Workshop: April 20, 2012 and April 26, 2013
The BMP partners hosted an annual workshop to teach contractors how to install small
scale BMP projects and utilize the resources and tools available to them through the BMP
retrofit process. Successful workshop participants were then placed on an annual BMP
Service Providers list. Both years, Tahoe RCD staff contributed to the workshop by offering
a series of 30 minute presentation which provided information and resources regarding
the integration of vegetation into BMPs and properly selecting plant species based upon
property site analysis in addition to general workshop support to support speakers and
answer participant questions. Other topics presented at the workshop included: how to use
the new TRPA BMP online handbook, how to interpret a BMP plan, how to pass a final
inspection, how to avoid costly errors, seasonal high ground water, fertilizer and irrigation
management, and BMP maintenance and pre-treatment.
Tahoe Basin Watershed Education Summit
During the summer of 2012, Tahoe RCD staff executed the first ever Tahoe Basin
Watershed Education Summit (TBWES); a three day event that included High Schools from
around the Tahoe Basin, and included kids from the City of South Lake Tahoe and Kings
Beach communities. TBWES is a new program in the Lake Tahoe Basin creating teams of
high school students, teachers, and resource specialists for an extensive watershed
assessment in Blackwood Canyon (a secondary TMDL). The data collected by students
during the program will assist the US Forest Service with evaluating restoration efforts
performed in the area.
Through the Tahoe Basin Watershed Education Summit, students were involved in an
integrated experience combining community service, academic achievement,
environmental stewardship, and career exploration. They examined vegetation, soil, runoff
characteristics and water quality effects of past and present human use in the watershed,
and learned how BMPs can improve natural function. The students achieved all this
primarily through making geomorphic observations of stream channel characteristics or
stream cross sections throughout the watershed. Additionally students surveyed, mapped,
and removed terrestrial invasive weeds and learned about bird mist netting at select sites
in the project area.
Photo gallery is at - http://andygiordano.photoshelter.com/gallery/TBWES- 2012/G0000NyODE1dY4ys/
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March 2014 – NRCS FINAL REPORT Community Watershed Partnership Tahoe Resource Conservation District
Demonstration Gardens
The Tahoe RCD is an active partner in four different
demonstration gardens: Tahoe City Historic Fish Hatchery,
Lake Tahoe Demonstration Garden at Lake Tahoe
Community College and the Evans Family Garden in the
Angora Community. At these gardens community
members and visitors can come learn, enjoy and
contribute to our beautiful Lake Tahoe gardens. The
gardens illustrate successful, environmentally-friendly
landscaping techniques and provide a venue for
community inspiration and education.
The Tahoe RCD hosts community service learning events several times a year on any of the
gardens. The Tahoe RCD contributed a Demonstration Garden focused article to TRPA’s
quarterly newsletter and facilitated over 20 community service volunteer events. At the
gardens, the Tahoe RCD presented 7 green thumb gardening classes and coordinated 8
presentations with the Lake Tahoe Master Gardeners.
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March 2014 – NRCS FINAL REPORT Community Watershed Partnership Tahoe Resource Conservation District
Results
Outlined below are specific actions the Tahoe RCD implemented to meet CWP Program objectives.
These actions include a variety of community strategies because the CWP approach is a fairly new
concept. The information presented below is organized by four primary strategies used by the
Tahoe RCD: 1) Private Parcel Technical Assistance services, 2) Stakeholder and Community
Outreach, 3) Community Workshops and Forums, and 4) Community Science and Stewardship.
Private Parcel Technical Assistance
In alliance with NRCS and the TRPA, the Tahoe RCD accomplished measurable efficiency and
overall effectiveness in the implementation of water quality BMPs. This success was attributed to
the use of streamlined BMP plans, increased outreach efforts, workshops, and incentive programs
which offer free BMP evaluations and technical assistance to encourage homeowners to install
BMPs.
BMP technical assistance offered by Tahoe RCD staff includes BMP final inspections, BMP site
evaluation plans, BMP system sizing, BMP progress checks consultations explaining TRPA’s
ordinance, soil tests, turf conversion, landscaping for defensible space, invasive weed, irrigation
and fertilizer management and issuing native plants and conservation materials.
BMP Assistance
According to the Chapter 60.4 of TRPA’s Code of Ordinances, all homeowners in the Tahoe basin
are required to install storm water BMPs on their property to infiltrate storm water and stop fine
sediment particles (<16µm) from reaching the lake and degrading Lake Tahoe’s famed clarity.
Tahoe RCD staff provides BMP assistance to single family homeowners and contractors in
California to help homeowners come into compliance with this ordinance. Photos of common
storm water BMPs are shown below.
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March 2014 – NRCS FINAL REPORT Community Watershed Partnership Tahoe Resource Conservation District
Driveway runoff conveyed by slotted channel drain to infiltration system (left) erosion control under deck (right).
Program efficiencies made meeting the minimum required deliverable for 233 BMP plans and 266
BMP technical assistance events possible. Under this grant, 526 unique private properties
received BMP assistance.
For reporting purposes, BMP assistance is categorized as a BMP plan or BMP technical assistance.
A BMP plan is a complete site specific design that once implemented and inspected for completion,
results in a TRPA BMP Certificate. A BMP technical assistance is typically defined as an event
where Tahoe RCD staff conducts a site visit to contribute to the overall BMP design or
implementation of the design through soil testing, site analysis, infiltration system sizing,
revegetation guidance, or BMP installation final inspection. When BMP technical assistance is
provided at a property that is also receiving or has received a BMP plan or other form of BMP
assistance, that assistance event is not represented as a required deliverable. Documenting
deliverables in this manner represents the actual number of private properties assisted instead of
the number of times assistance was provided.
Offering cost free BMP assistance and direct outreach in the CWP areas assisted the District in
reaching the required deliverables. Of the 526 properties assisted, 66 resulted in BMP Certificates
while only 3 of those certificates were the installation results of BMP plans developed during the
same grant reporting period. When a property is BMP certified and the BMPs are maintained for
function, it is assumed that sediment and/or runoff no longer leaves the property. Through
utilization of the NRCS BMP Calculation Spreadsheet, soil erosion savings can be estimated for the
66 properties certified for BMPs. If the average impervious surface of each property is 2,070
square feet, an estimated 1,657 pounds of sediment will be kept from polluting Lake Tahoe
waterways each year. A summary of technical services is included in Appendix C and D. A
summary table of the project deliverables can be seen in Figure 7.
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March 2014 – NRCS FINAL REPORT Community Watershed Partnership Tahoe Resource Conservation District
Project
Deliverables
Summary
Total Service
Provided (#)
Minimum Service
Required (#)
Service within
CWP Area (#)
Service within
CWP Area (%)
BMP Plans 235 233 157 67%
BMP Technical
Assistance
291
(66 technical assists
resulted in BMP
certificates)
266
118
41%
Figure 7: Summary Table of Project Deliverables
Aside from the incentive of offering free BMP assistance to homeowners in the CWP areas,
meeting required deliverables was augmented through focused TRPA’s BMP outreach to non-BMP
compliant properties and the District’s BMP outreach to select properties exhibiting signs of
seasonal high groundwater. Twenty-three of the 235 BMP plans were delivered in the Al Tahoe
Community in South Lake Tahoe through collaboration with TRPA. The properties were selected
because they were determined to contribute higher than average loading of fine sediments and
other pollutants to local water bodies. An additional 37 of the 235 BMP plans were delivered to
properties identified by NRCS and Tahoe RCD as site constrained through vegetative indicators of
high groundwater. These properties are constrained for stormwater infiltration systems to avoid
potential groundwater contamination. BMP recommendations for these sites typically do not
require site specific BMP design and BMP recommendations are limited to source control methods
such as erosion control through slope stabilization, driveway paving, and soil protection with rock,
organic mulch and vegetation. The Wet Soil BMP Plan template is attached in Appendix E.
Community Science and Stewardship Activities
A major component of the Community Watershed Partnership is fostering a sense of community
and forging a connection to our watersheds, which Tahoe RCD has promoted though it’s
community science and stewardship activities. Community science projects promote awareness of
the environment, engage community members in the scientific process, and help educate the
public about ongoing environmental issues all while collecting real data. Community stewardship
activities were a great opportunity for community bonding while providing environmental
education and conservation. Activities performed under this grant follow.
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March 2014 – NRCS FINAL REPORT Community Watershed Partnership Tahoe Resource Conservation District
Soils Investigation for Storm water Infiltration: June 2012
A soils assessment focusing on suitability of public lands for storm water infiltration was
conducted within the South –“Y” and Sierra Tract neighborhoods located within the South
Lake Tahoe CWP area. The NRCS lead this effort to assist the Tahoe RCD with this project
providing leadership and technical assistance. This project was achieved utilizing GIS map
layers to find possible sites, testing soil infiltration rates, depth to seasonal high
groundwater and fragipan, and a vegetative assessment. The project goal was to contribute
data to an inventory that will allow for detailed site-specific soils information for NRCS,
City of South Lake Tahoe and other public agencies looking for stormwater treatment
opportunities. Tahoe RCD, NRCS and Tahoe Baikal Institute instituted this week long
project. The project report is included in Appendix F.
Streamkeepers
Tahoe RCD staff led an effort to engage community volunteers and local agency staff from
the California Tahoe Conservancy, and California Trout to execute two separate South Lake
Tahoe Streamkeepers Citizen Monitoring Events. Streamkeepers was developed in attempt
to better educate and engage community members of South Lake Tahoe in the monitoring
of their local watersheds through a series of annually reoccurring volunteer monitoring
events. The mission of the Streamkeepers Monitoring Group is to promote community
stewardship through education, collaboration, and action. A total of 10 volunteers and 4
Tahoe RCD staff members monitored water quality, macro invertebrates, stream bank
stability, substrate classification, habitat value, and bank cover in three monitoring reaches
along Trout Creek in the South Lake Tahoe CWP area (Figure 8). Three sample reaches
were identified, and are shown in the map below. The full Streamkeepers monitoring
report is included in Appendix G.
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March 2014 – NRCS FINAL REPORT Community Watershed Partnership Tahoe Resource Conservation District
Figure 8: 2012 Streamkeepers Monitoring Reaches
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March 2014 – NRCS FINAL REPORT Community Watershed Partnership Tahoe Resource Conservation District
Snapshot Day
The Tahoe and Truckee River Snapshot day is a prime example of citizen monitoring in
action. Every year, hundreds of volunteers help measures pH, temperature, dissolved
oxygen, turbidity, stream flow, conductivity, total dissolved solids, fecal coliform, nutrients,
nitrogen, phosphorus and visual assessments of stream throughout the Tahoe and Truckee
watersheds. This year’s event was held on May 12, 2013 and marked the 13th anniversary
of the event. The South Shore event was
organized by Tahoe RCD in collaboration
with the League to Save Lake Tahoe, the
North Shore and Truckee River events were
organized by Incline Village General
Improvement District, Nevada Department
of State lands, Truckee River Watershed
Council, and the Piute Tribe. Tahoe RCD
staff assisted with project planning,
equipment calibration, and volunteer
recruitment. Within the Tahoe and Truckee
watersheds there were a total of 390 volunteers at 90 monitoring sites (Figure 9). There
were over 75 volunteers from the community and local resource agencies that participated
in the water quality monitoring activities at 33 sites along the South Shore. The 13th annual
Snap Shot Day for 2013 monitoring report can be found at http://snapshotday.org/wp-
content/uploads/2013/09/2013-SSD- Report-Final.pdf
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March 2014 – NRCS FINAL REPORT Community Watershed Partnership Tahoe Resource Conservation District
Figure 9: 2013 Snapshot Day Monitoring Sites in the Lake Tahoe Basin
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March 2014 – NRCS FINAL REPORT Community Watershed Partnership Tahoe Resource Conservation District
Community Invasive Weed Mapping and Removal
Tahoe RCD staff led the effort to mobilize community
volunteers and Tahoe Basin AmeriCorps members for
identification, mapping, treatment and control of invasive
plants at select urban stream environment zones of Trout
Creek and the Upper Truckee River in South Lake Tahoe,
CA. Two community weed pulls were executed in August
and September during the summer of 2012. A total of
seven community volunteers, 24 AmeriCorps members,
and four TRCD staff members surveyed 255 acres within
the selected locations. The group mapped 6,032 invasive
weeds and treated 3,720 of them. Mapping and control
data was presented to The Lake Tahoe Basin Weed
Coordinating Group and the EL Dorado County Department
of Agriculture for all occurrences within the Community
Watershed Partnership area selected for 2012. See Figure 10 for the mapped invasive
weeds and Appendix H for a table of the survey extent, location and description of invasive
species.
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March 2014 – NRCS FINAL REPORT Community Watershed Partnership Tahoe Resource Conservation District
Figure 10: 2012 Tahoe RCD Invasive Plant Mapping
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March 2014 – NRCS FINAL REPORT Community Watershed Partnership Tahoe Resource Conservation District
Project Partners and Stakeholders
The CWP initiative involves many stakeholders and partner agencies. Any given watershed area
within the Tahoe Basin typically includes a variety of landowners, land managers, residents and
stakeholder groups. Partners include but are not limited to:
Local Community Members & Residents
El Dorado and Placer Counties
Municipalities, such as South Lake Tahoe, Kings Beach and Tahoe City
US Forest Service
California Tahoe Conservancy
Local Fire Districts
Caltrans
Tahoe Regional Planning Agency
Lahontan Regional Water Quality Control Board
Local Public Utility Districts
University of California and Nevada Cooperative Extension
Local non-profits
Beyond BMPs, landscape conservation, and stewardship, a major focus of the CWP is to bring
together agency representatives to discuss on-going or upcoming environmental restoration
projects within the target watershed areas and determine cost effective methods for working
across ownership and jurisdictional boundaries. Through this collaborative process the Tahoe
RCD can draw upon common values, interests, and opportunities in preserving Lake Tahoe.
The CWP process also provides a forum for agency representatives to share information with local
community members on the goals and expected implementation timeframes of larger scale EIP
projects and how these may provide opportunities and benefits within the selected watershed
areas. Outreach activities, neighborhood conservation events and interactive forums conducted
within targeted watershed areas throughout the Tahoe Basin also raise awareness amongst
community members and increase the understanding and support for restoration and
conservation efforts.
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March 2014 – NRCS FINAL REPORT Community Watershed Partnership Tahoe Resource Conservation District
Lessons Learned
While the implementation of conservation measures and community awareness of local
environmental issues in the Tahoe Basin have seen measurable increases since the signing of this
grant agreement, the established partnership is always seeking new methods of working with the
community to facilitate on-the-ground conservation practices. The current decline in funding for
implementation of such practices will mean that project proponents and stakeholder groups will
need to continue to explore opportunities to find efficiencies, share existing resources, and reduce
overall project costs related to conservation driven initiatives.
Some of the programmatic changes instituted to improve efficiencies include:
Targeting large successful public gathering events to increase community participation
Targeting education and outreach efforts through stewardship events
Performing database improvements
Simplifying BMP plans when soil conditions permit
Providing in office technical assistance to property owners through photo documentation
The Tahoe RCD also recognizes that landscape consultations were an ideal opportunity to assist
homeowners with conservation issues pertaining to their properties and their specific
communities. Once on site, Tahoe RCD staff could relate landscaping practices to erosion control
and storm water BMPs, invasive weeds, fertilizer and irrigation management integrating
conservation practices in a way that encouraged stewardship through education. This type of
technical assistance seems to resonate with community members and increased on-site technical
assistance requests. Ultimately there is balance between finding program efficiencies and quality
outreach to property owners.
Future Program goals include:
Continued planning and implementation of area-wide treatment of stormwater in targeted
watersheds to meet TMDL/EIP needs
Provide natural resource technical assistance, leadership and education
Increase community participation in landscape conservation, targeted BMP
implementation, defensible space practices, invasive weeds control and fertilizer and
irrigation management
In final summary, funding from this grant has allowed the Tahoe RCD to reach thousands of
residents and visitors through newsletters, radio broadcast, and mailers. It enabled direct
technical assistance to over 290 landowner’s, over 200 BMP plans, and 66 final BMP certificates.
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March 2014 – NRCS FINAL REPORT Community Watershed Partnership Tahoe Resource Conservation District
This work contributed to pollutant load reductions estimated at greater than 1,600 pounds of
sediment per year. The Tahoe RCD also facilitated and organized several environmental
stewardship events which engaged hundreds of volunteers in water quality sampling and invasive
weed removal. Over 33 tributaries were monitored on the south shore of Lake Tahoe, and 255
acres of terrestrial weeds were mapped, with over 3,000 weeds manually removed by volunteers.
Appendix A: CWP Brochure and Flier
Appendix B: Community Watershed Partnership 2012 Survey Results
The Lake Tahoe Community Conservation Survey was designed as a tool to help the Tahoe Resource
Conservation District (Tahoe RCD) better serve neighborhoods around the Basin through the Community
Watershed Partnership (CWP) program.
Surveys were conducted during the summer and early fall of 2012 at CWP neighborhood BBQ events, local
farmers’ markets, and additional partner outreach events throughout the North Shore and South Shore
communities on the California side of the Basin. Surveys were administered hardcopy, online and via
smartphone, with a total of 84 participants.
The primary focus of these surveys is to identify the environmental priorities of Lake Tahoe residents while
developing a better understanding of our unique communities of interest. The Tahoe RCD is specifically
interested in the public’s level of knowledge and interest in our programs, as well as the level at which residents
will fund and or participate in stewardship events. Survey results also allow the Tahoe RCD to discern
differences between the North, South and West Shore communities. After comparing survey results, we found
the following trends to be of particular interest and with the potential to inform future project planning:
Public awareness of Tahoe RCD programs: 83.3% of all surveyed participants were aware of the Tahoe RCD, with the top three most well-known programs being watercraft inspections; AIS control projects and BMP assistance. CWP was the least well-known at 27.6%. This response is not surprising in that CWP is a fairly new program for the Tahoe RCD; incorporating CWP messaging into more widely-recognized programs could be a strategy for improving community exposure.
Primary environmental concerns in the community: The top ranking environmental issues were: (1st)
lake clarity, (2nd) fire/fuels thinning, and (3rd) invasive species. While much of CWP tasks relate directly
to lake clarity, little focus has been placed on fire concerns. There is potential to reap benefits in
community engagement through CWP by addressing those concerns, perhaps by partnering more
closely with the fire districts.
Specific community interests in supporting conservation: By far (62.5%), those surveyed were most
interested in learning more about stewardship events (trail maintenance, watershed monitoring, weed
pulls, and plantings, etc.) as a way to get involved in local conservation. The top four stewardship
activities of interest were: (1st) educational events, (2nd) invasive species control, (3rd) invasive species
control, and (4th) trail maintenance. The second-most popular community engagement interest, at
37.5%, was contributing supplies or volunteer hours to community workdays. About 31% of those
surveyed were interested in learning more about shared stormwater treatment opportunities.
Generally, these results seem to suggest that direct-action community engagement activities with fairly
immediate results, such as school program volunteering, weed pulls and outdoor recreation
improvements, are ideal for capturing public interest.
Financial support for conservation: Over a quarter (28.6%) of the participants responded that they
could not afford to financially support not-for-profit causes. However, the majority of respondents
acknowledged that they were willing to volunteer or offer in-kind donations for projects. Perhaps the
most effective use of public support would be in accomplishing on-the-ground work with volunteer
muscle (weed pulls, school programs, watershed monitoring, etc.). Only 3 of the survey participants
were business owners, making it unreasonable to draw any conclusions on best strategies for building
sustainable sponsor partnerships. It may be worthwhile to develop a survey targeting that demographic
specifically.
Trends between the Basin communities: Not all those surveyed noted which Tahoe Basin community
they most identified with, and some surveyed were non-residents, leaving the data set for comparing
communities at 48 responses. 2 of these responses were from West Shore residents; a data set small
enough that we are not considering it in this analysis. Significant differences between the North and
South Shore communities included:
o Knowledge of Tahoe RCD: 17% of North Shore participants were unaware of the Tahoe RCD,
while only 3% in the South Shore were unaware. This would suggest an increased
branding/general outreach effort may be warranted on the North Shore. Notably, BMP services
and watercraft inspections were the most well-known Tahoe RCD programs in both
communities.
o Community engagement interests: In both communities, the greatest percentage of those
surveyed were interested in stewardship events as a way to get involved in conservation efforts.
However, on the North Shore, participants showed equal interest in shared stormwater
treatments as in stewardship events; on the South Shore, shared stormwater treatments ranked
second, below stewardship. The North Shore participants also indicated a greater interest in
donating funds to conservation projects.
o Financial support preferences: A far greater percentage of the South Shore participants, at 31%,
indicated they could not afford to financially support non-profit causes, compared to 13% of the
North Shore participants. A greater percentage of North Shore participants, at 25%, indicated a
preference for supporting environmental causes, in comparison to 19% of the South Shore
participants. Community causes were also ranked higher (38%) in the South Shore, than in the
North Shore (25%). The North Shore community also expressed an interest in religious causes
(12%), while none of the South Shore participants showed an interest in the category.
Overall Results
Yes 83%
No 17%
Percent of participants aware of Tahoe RCD
Boat Inspections, 85.7
BMPs, 73.8
Conservation Landscaping, 57.1
AIS, 75.0
Terrestrial Invasive Species, 50.0
K-12 Education,
33.3
CWP, 25.0
Percent of surveyed public aware of Tahoe RCD by program
0
100
200
300
400
500
600Environmental Priorities (weighted scores)
0
5
10
15
20
25
30
35
Community engagement preferences
# Surveyed
Trail maintenance
13% Watershed monitoring
10%
ISP Control 14%
Tree plantings
12%
Educational events
15%
Community Work Days 14%
Community Garden
9%
Volunteering at kid events
9%
Fundraising events
4%
Stewardship activity preferences, by percent of participants
Community Ed & Outreach (k-12)
23% Scholarships for youth &
community projects
6% Outdoor sports-focused
fundraisers 19%
Specific community
conservation projects
10%
Conservation improvements for
disadvantaged residents
8%
Neighborhood events
16%
ISP Contol and Prevention
18%
Financial support preferences, by percent of participants
North Shore Results
Yes 83%
No 17%
Percent of N. Shore participants aware of Tahoe RCD
Watercraft Inspection
23%
BMP and Erosion Control
Assistance 21%
Conservation Landscaping for
homeowners and residents
12%
Aquatic Invasive Species
Control/Monitoring
16%
Invasive Species
Removal 12%
Community Watershed Partnership
8%
Environmental Education (K-12) and Community
Outreach 8%
Percent of N. Shore participants aware of Tahoe RCD, by program
0102030405060708090
Environmental issues of greatest concern to N. Shore participants (weighted score)
0
1
2
3
4
5
6
Community engagement preference on the N. Shore, by number surveyed
Trail maintenance
12%
Watershed monitoring
9%
Invasive species control
10%
Tree plantings 12%
Educational events
14%
Community work days
14%
Volunteering in a community
garden 10%
Volunteering for kids events
14%
Fundraising events for
conservation issues
5%
Stewardship interests by percent of N. Shore participants
I prefer to support social
causes 25%
I prefer to support
environmental causes
25%
I prefer to support local community
causes 25%
I prefer to support religious
causes 12%
*No participants indicated that they have no
interest in supporting non-
profit causes
I cannot afford to support not-for-
profit causes
13%
Financial support preferences by percent of N. Shore participants
South Shore Results
Yes 97%
No 3%
S. Shore participants aware of Tahoe RCD
Watercraft Inspection
20%
BMP and Erosion Control
Assistance 18%
Conservation Landscaping for
homeowners and residents
16%
Aquatic Invasive Species
Control/Monitoring
19%
Invasive Species Removal
12%
Environmental Education (K-12) and Community
Outreach 9%
Community Watershed Partnership
6%
Percent of S. Shore participants aware of Tahoe RCD, by program
0
20
40
60
80
100
120
140
160
180
Environmental issues of greatest concern to S. Shore participants (weighted score)
0
2
4
6
8
10
12
Community engagement interests on the S. Shore, by number of individuals
Trail maintenance
11%
Watershed monitoring
13%
Invasive species control
16%
Tree plantings 7%
Educational events 16%
Community work days 13%
Volunteering in a community garden
8%
Volunteering for kids events
10%
Fundraising events for conservation
issues 6%
S. Shore stewardship interests, by percentage of participants
I prefer to support social causes
12%
I prefer to support environmental
causes 19%
I prefer to support local community
causes 38%
* None of the responding participants
indicated that they do not donate to
non-profit causes, or that they prefer
to donate to religious causes
I cannot afford to support not-for-
profit causes 31%
Financial support preferences by percent of S. Shore participants
Appendix C: Technical Assistance Summary Table
Appendix D: BMP Plan Summary Table
Appendix E: Wet Soils BMP Plan Template
August 27, 2013 Dear Homeowner, The Tahoe Resource Conservation District (Tahoe RCD) has developed this informational packet to assist you with implementing Best Management Practices (BMPs) on your property. This information will help you to comply with Chapter 60 Section 60.4 (Best Management Practices Requirements) of the Tahoe Regional Planning Agency (TRPA) Code of Ordinances. We are contacting your today because your property falls within our 2013/2014 Community Watershed Planning area and we are currently funded to offer you BMP technical assistance. This summer, from the roadside, Tahoe RCD field technicians were able to visually verify property soil characteristics which qualified your property for the enclosed BMP Retrofit Plan. The Best Management Practices Retrofit Ordinance requires landowners to infiltrate stormwater runoff, stabilize eroding soil, rehabilitate disturbed soil areas, and pave approved roads, driveways and parking areas. However, due to the acknowledged presence of slowly draining soils that compromise the ability for natural infiltration and/or the presence of soils within close proximity to high ground water, stormwater infiltration treatments cannot be recommended for runoff associated with your property. The presence of these conditions makes your property site constrained for stormwater infiltration BMPs. Enclosed are BMP Treatment Descriptions detailing those treatment options available for your property. This generic BMP packet was created to guide you or your contractor through the process of BMP design and implementation. The information in this packet is property-specific and only relates to BMP treatments on properties that have been identified as site constrained by a Tahoe RCD field technician. If you are using a contractor to install your BMPs, please be sure to supply them with all of the enclosed information. Before you install your BMPs, refer to the Living with Fire guidelines to be sure that the recommended BMP treatments are not in conflict with the most current fire defensible space requirements. You may also request a free fire defensible space inspection by calling the respective fire district that your property exists within. Before and During Construction:
• Read through and provide your contractor with all enclosed documents • Utilize Lake Tahoe Standard Drawings for specific BMP treatment requirements
Before you request a final BMP inspection: • Refer to the BMP Final Inspection Checklist to insure the completed work meets the minimum
requirements for TRPA’s BMP Ordinance • Submit the Authorization to Release BMP Site Evaluation Information form to Tahoe RCD
Provide to the BMP final inspector: • Approved BMP plans if the infiltration systems were not designed by the Tahoe RCD
When you are ready for a BMP final inspection or further technical assistance, please utilize the online Service Request Form located at http://tahoercd.org/contact-tahoe-rcd/. Please contact me if you have any questions. Respectfully, Sarah Bauwens, Watershed Resources Intern Phone: 530-543-1501 (ext.126) [email protected] Enclosures BMP Treatment Descriptions BMP Retrofit Site Plan (sample) BMP Design and Installation Considerations Site Constraint Tracking Form Lake Tahoe Standard Drawings Brief Soil Descriptions (Tahoe) Materials Calculator Authorization to Release BMP Site Evaluation Information Form Yard Fertility Management BMP Final Inspection Checklist
Dear Tahoe Basin Property Owner:
Thank you for your interest in participating in the BMP Retrofit Program! We value your partnership and willingness to work with us to protect Lake Tahoe.
At this time, we have found that your property includes site characteristics (such as high groundwater, slow permeability soils, or rocky soils) that make BMP Retrofit very difficult in terms of stormwater capture and infiltration. Therefore, we recommend that stormwater infiltration BMPs not be installed on your property. Instead, please refer to the attached report outlining the erosion control measures that should be installed on your property.
Once you have completed all erosion control measures for your property, please contact us at 775/589-5202. You will be eligible to receive a “Source Control Certificate.” This Certificate demonstrates to TRPA that you have done everything possible to comply with the requirements of the BMP Retrofit Program (Chapter 60.4, TRPA Code of Ordinances).
TRPA is currently exploring options on how to equitably remedy existing difficult retrofit situations so that all property owners in the Tahoe Basin can help control stormwater runoff. Once an appropriate solution has been identified and approved, TRPA will contact you and explain how you can complete the BMP retrofit process to receive a full BMP Certificate of Completion.
Please be aware that as long as you maintain all erosion control BMPs on your property and have a Source Control Certificate, TRPA will not pursue enforcement action for noncompliance with the BMP Retrofit Program. Again, once an equitable solution has been identified, TRPA will outline the process to bring your property into full compliance with Chapter 60.4 and receive a Certificate of Completion.
We appreciate your patience regarding this matter and thank you for doing your part to protect Lake Tahoe. Sincerely,
Brian Judge Principal Environmental Specialist Environmental Improvement Program Acting Stormwater Management Team Leader
Site Constraint Tracking Form
Property Address: County: APN:
Site Evaluator: Agency: Date:
Tahoe RCD
The following site constraint(s) has/have been identified on your property:
Property located in an area with a Seasonal High Water Table/Stream Environment Zone
Property located on slow soils (Ksat ≤1”/hr)
Property located on rocky soils or in an area with bedrock at or near grade
Infiltration area restricted due to utility placement
Infiltration area restricted due to retaining structures
Steep slopes / Cut and fill slopes
Infiltration area restricted due to property boundaries
Conveyance structure cannot be installed due to underground heating unit
Structure located with no/minimal setback to public right-of-way
Evaluator Notes:
Considerations while addressing Best Management Practices Soils: The Tahoe Resource Conservation District (Tahoe RCD) uses the Natural Resources Conservation Service (NRCS) Soil Survey to determine the soil type for properties in the Lake Tahoe Basin. This information is then used to assess the ability of soils to naturally infiltrate runoff and recommend Best Management Practices (BMPs). Please refer to the enclosed Brief Soil Descriptions for more information regarding this property’s soil type. Groundwater: Tahoe Regional Planning Agency water quality regulations prohibit BMPs from being installed within one foot of seasonal groundwater levels. Property Lines: BMP treatment systems must be installed within the property boundary limits. The Tahoe RCD does not establish property boundary lines. Before installing BMPs, confirm property boundary lines and any setback requirements established by your local building or planning departments. Fire Defensible Space: Tahoe RCD staff and the Natural Resources Conservation Service do not have the authority to perform fire defensible space inspections. Fire defensible space information is included with these BMP prescriptions as a courtesy to the Fire Protection Districts. All references and prescriptions for defensible space were provided by the Lake Tahoe Fire Prevention Officers. Through cooperation with the Tahoe Regional Planning Agency, Tahoe Resource Conservation District, Nevada Tahoe Conservation District, Natural Resources Conservation Service, and University of Nevada Cooperative Extension, efforts have been taken to provide a conservation plan and BMP designs that are compatible with Living with Fire guidelines. The final determination that landscaping and BMPs installed for water quality purposes meet defensible space requirements lies solely with the fire protection districts that have the proper authority. Note that BMP minimum treatment dimensions do not always encompass the 0 to 5 foot non- combustible area. Therefore, the Materials Calculator can be used to determine quantities for drain rock armoring that will also meet the defensible space criteria. Refer to Living with Fire – Lake Tahoe Basin Second Edition for more information regarding maintaining a fire defensible landscape while planning BMP implementation. Please contact the local fire district or department for defensible space requirements and recommendations: Lake Valley FPD (530) 577-2447 South Lake Tahoe FD (530) 542-6160 North Tahoe FPD (530) 583-6913, Fallen Leaf FD (530) 542-1343, Meeks Bay FD (530) 525-7548 Underground Utilities: Before excavating soil for the installation of BMPs, it is imperative that underground utilities be located and marked on the property to avoid damage or service interruption during construction. According to Government Code 4216, the individual conducting excavation is responsible for notifying utilities before digging. Underground Service Alert (USA), the one call system, enables this notification. Call 811 at least two full working days and not more than 14 days before any excavation occurs. Additional information is available at www.usanorth.org. Drainage: If stormwater from neighboring public or private properties flows onto the property, contact the local jurisdiction for technical assistance or more information. A licensed engineer may need to be consulted to develop an appropriate solution that protects structures from potential water damage. TRPA Coverage: It is advisable to document existing conditions before making any changes to the property to avoid losing existing coverage rights. For information on land capability and land coverage, please visit www.trpa.org. Grading and Temporary BMPs: Tahoe Regional Planning Agency (TRPA) regulations state that between October 15th and May 1st it is prohibited to grade or excavate more than 3 cubic yards of soil. Installation of temporary BMPs is also required on all sites where the vegetation and soil will be disturbed. Temporary BMP practices will help prevent sediment or contaminated water from leaving the site during construction activities. Temporary BMPs are site-specific, must be constantly maintained, and are usually good for only one year or one winter season. Temporary BMPs should be
installed before starting construction and must be maintained until all construction activity is completed and/or until permanent BMPs are installed. In order to maintain properly functioning temporary BMPs, systems should be checked immediately before an impending storm as well as after the storm has passed. Materials: The Tahoe RCD recommends the use of 3/4 inch to 1-1/2 inch washed drain rock; however, any kind of rock can be utilized to achieve desired aesthetic and use characteristics for the property. You may even use rock found on the property to create a more natural look and to reduce the cost of BMP installations. Maintenance Considerations: Construct a border around drain rock treatments to contain materials and reduce maintenance. Economical border materials include used lumber, small logs, or cobble-sized rock found on site. Materials such as pressure-treated wood, landscape edging, and/or one of the many recycled composite products available can also be utilized. If using any type of flammable material, ensure that these materials do not connect to the structure to help protect the structure from fire. Over time, infiltration systems fill in with sediment and fail; therefore, maintenance is required to keep these systems functioning properly. Visually check BMPs after major storms, in the spring, and just before winter to ensure they are working properly. For more information on BMP maintenance, visit the TRPA Stormwater Management Program at http://www.tahoebmp.org/. Structural Integrity: To the maximum extent allowable by law, the property owner agrees to indemnify, defend, and hold harmless Tahoe RCD, its Board of Directors and its employees (collectively, Tahoe RCD) from and against any and all suits, losses, damages, injuries, liabilities, and claims by any person (a) for any injury (including death) or damage to person or property or (b) to set aside, attack, void, modify, amend, or annul any actions of Tahoe RCD. The foregoing indemnity obligation applies, without limitation, to any and all suits, losses, damages, injuries, liabilities, and claims by any person from any cause whatsoever arising out of or in connection with either directly or indirectly, and in whole or in part (1) the processing, conditioning, issuance, or implementation of these recommendations; (2) any failure to comply with all applicable laws and regulations; or (3) the design, installation, or operation of any improvements, regardless of whether the actions or omissions are alleged to be caused by Tahoe RCD or Property Owner. Included within the Property Owner's indemnity obligation set forth herein, the Property Owner agrees to pay all fees of Tahoe RCD’s attorneys and all other costs and expenses of defenses as they are incurred, including reimbursement of Tahoe RCD as necessary for any and all costs and/or fees incurred by Tahoe RCD for actions arising directly or indirectly from issuance or implementation of these recommendations. Property Owner shall also pay all costs, including attorneys’ fees, incurred by Tahoe RCD to enforce this indemnification agreement. If any judgment is rendered against Tahoe RCD in any action subject to this indemnification, the Property Owner shall, at its expense, satisfy and discharge the same. Photographic Records: Beginning May 1, 2009 a photographic record is required of all BMP installations that entail backfilled excavations on a homeowner’s property. Expiration after 3 years: Beginning May 1, 2009 all evaluations will expire three years from the date the evaluation was conducted. If homeowners do not complete the recommended BMP installation treatments within this three year time frame, they will be required to call the appropriate agency and have the evaluation reviewed and, if necessary, revised. This will ensure that all homeowners are incorporating the most current technology and Best Management Practices treatments on their property.
Online Resources TRPA Stormwater Management www.tahoebmp.org • BMP Sizing Worksheet • BMP Property Status Search • BMP Handbook
• BMP Materials and Providers Lists • Lake Tahoe BMP Standard Drawings/Installation Guidelines • BMP Contractors Handbook • Real Estate Disclosure Form • Fertilizer Use Information
• Home Landscaping Guide for Lake Tahoe and Vicinity TRPA www.trpa.org • Site Assessment Application • Land Coverage/Land Capability Information • Permitting Information/Application • Combining BMPs and Defensible Space Information Fire Defensible Space • Living with Fire in the Lake Tahoe Basin Website and Publication http://www.livingwithfire.info/tahoe/ • Public Resource Code 4291: http://www.fire.ca.gov
Tahoe Resource Conservation District www.tahoercd.org • Lake Tahoe BMP Standard Drawings/Installation Guidelines • Backyard Conservation Tip Sheets • Calendar of Events • Dirt Driveway Roadmaps • Home Landscaping Guide for Lake Tahoe and Vicinity • BMP Materials Calculator • Release Authorization Form
Best Management Practices Treatment Descriptions For Properties with Slowly Draining and/or Wet Soil
Revised 7/17/2013
According to the Tahoe Regional Planning Agency (TRPA) Best Management Practice (BMP) retrofit ordinance chapter 60 section 60.4, all homeowners are required to capture and infiltrate runoff generated from impervious surfaces for the protection and restoration of water quality. However, due to the acknowledged presence of slowly draining soils that compromise the ability for natural infiltration, stormwater infiltration treatments cannot be recommended for runoff associated with your property; instead sediment source control treatments are recommended for property address. Section 60.4.8.B of the ordinance describes these special circumstances as site constraints, and acknowledges that complete infiltration is not possible on all parcels. Although infiltration BMPs cannot be recommended for this property, sediment source control BMPs can still be implemented; information contained within this packet solely pertains to those BMPs that address sediment source control. Please be aware that a BMP Certification of Completion for the property cannot be issued until the TRPA has identified and approved an appropriate solution for the site constraint present on this property. However, homeowners are encouraged to complete all recommended sediment source control treatments.
To learn more about the ordinance, visit www.tahoebmp.org. Visit the Tahoe RCD website at www.tahoercd.org to download the most current tip sheets and BMP Standard Drawings and Installation Guidelines. Complete implementation of these source control BMPs will meet the requirement to receive a Source Control Certificate after a final inspection is completed on the property by Tahoe RCD field technician. Please note that this BMP Retrofit Evaluation Packet can only be utilized by specific properties that have been identified as site constrained by a Tahoe RCD staff member, and cannot be utilized on a property that has not received this identification. If you have any questions regarding the application of specific treatments on your property, please call the Tahoe RCD Conservation line at (530) 543-1501 x 113 to discuss available options. Soil and Landscape Areas Although bare ground may be effective in reducing wildfire threat around the property, there are other options to help stabilize soil. Please be aware that excessive bare ground may increase the soil erosion potential of the property and contribute to the decline in the water clarity of Lake Tahoe. Options to treat bare soil on the property include, but are not limited to, establishing a mosaic of vegetation and mulch. Combustible mulch should not be used in a widespread manner within 30’ of the structure. Sloped sites may require mechanical stabilization methods such as installing retaining walls, rock riprap slope protection and terracing. Request a conservation landscaping consultation, utilize the Home Landscaping Guide for Lake Tahoe and Vicinity and utilize our online resources to learn more about landscaping and combining BMPs with defensible space in your landscape. Contact the local fire district for information on acceptable defensible space treatment options for your specific property and review the online resource Living with Fire-Lake Tahoe Basin. Restore compacted bare soil areas If areas on your property have been compacted by vehicular traffic, the soil in these areas should be covered with 2 inches of compost and then tilled to a depth of 6 to 8 inches. This will greatly increase the survival rates for seeds sown and vegetation planted. A combination of native or adapted vegetation and mulch produces a low
maintenance landscape that is highly effective at preventing erosion. There are many native and adapted grasses, plants, shrubs, and trees that can be used. Please review the recommended plant list in chapter 7 of the Home Landscaping Guide help identify species to suit individual property and landscaping goals. In order to prevent future soil degradation, parking barriers can be installed to restrict vehicular access to restored areas. Parking barriers can be made from a variety of materials such as split rail fencing, boulders, wood posts, or shrubs. Refer to Lake Tahoe Standard Drawing BMP-026 for more information on parking barriers. It is advisable to document existing conditions before making any changes to the property to avoid losing existing coverage rights. For information on land capability/land coverage please visit www.trpa.org. Refer to the enclosed Paving Residential Dirt Driveways handout for more information. Drip Lines Stormwater falling from roof surfaces onto bare or poorly vegetated soils detaches sediment particles and causes noticeable erosion. To satisfy the BMP retrofit ordinance, potential erosion from roof runoff must be managed on the property. The options outlined below are commonly used methods to manage roof runoff. Select the best options for your property. For all drip line installations, treatments must extend a minimum of 6” inside of the drip line and extend a minimum of 12” beyond the drip line of a single story roof, 18” beyond the drip line of a 2-story roof, and 24” beyond the drip line of a 3-story roof. Border the treatment to retain the material and exclude adjacent soil. Option 1: Armor bare soil under drip line with 3” layer of drain rock or cobble and border system; Refer to Lake Tahoe Standard Drawing BMP-009 & BMP-002 Install drain rock or cobble directly under the drip line to armor the soil in this area. Before applying rock under drip lines, it is important to break up the existing soil with a hard rake or shovel. When the receiving area of the property slope exceeds 15%, utilize riprap for soil protection. Refer to Lake Tahoe Standard Drawing BMP-009 for specific requirements and construction considerations. Low growing, irrigated, herbaceous vegetation can be used in conjunction with rock armor. If utilizing a combination of vegetation and rock armor, please be aware that planter beds are required to meet the dimension standards listed in BMP-009 and require a border. Refer to the Living with Fire guidelines or contact the local fire district for acceptable mulching materials and methods. Option 2: Maintain existing vegetation/turf under drip line Vegetation under the drip line protects the soil from the impact of the concentrated roof runoff and promotes stormwater infiltration. An alternate treatment may need to be installed in this area if the condition of the vegetation changes. If utilizing turf or lawn, a border will not be required, assuming that the lawn is healthy and vigorous and excludes loose soil from the treatment. Vegetation in the drip line treatment area must be vigorous (exhibiting roughly 70% canopy cover within three feet of the soil surface), protect the entire treatment area, and persist from year to year. Rock mulch should be utilized to fill the void spaces between the vegetation to protect any bare soil. Option 3: Maintain or enhance existing vegetation under drip lines Vegetation under the drip line protects soil from the impact of the concentrated roof runoff and promotes stormwater infiltration. Vegetation in the drip line treatment area must be vigorous (exhibiting roughly 70% canopy cover within three feet of the soil surface), protect the entire treatment area, and persist from year to year. Rock mulch should be utilized to fill the void spaces between the vegetation to protect any bare soil. If the vegetation in the area receiving runoff does not meet the above standards, maintain or enhance the existing vegetation until it does so.
Refer to online resources, Tahoe Native and Adapted Plants and the Home Landscaping Guide, for plant selection, planting, and care instructions. Examples of adequate vegetation include: • Maintained grasses or turf that has been established directly up to the foundation • Low growing non-woody (herbaceous) perennials and annuals with minimal bare soil exposed Option 4: Gutter conveyance system Gutter conveyance systems need to remain in good repair and clear of debris in order to remain functional. Redirect and/or extend any gutter downspouts so the energy generated by roof runoff can be dissipated and not discharged directly to bare soils where the potential for erosion is high. The installation instructions for this treatment depend on the product purchased; please refer to product specifications. If there is currently a gutter conveyance system installed on the house, install an energy dissipater under the gutter downspout. To do this, armor the runoff receiving area with rock or adequate vegetation to promote infiltration and minimize erosion. There are many options to dissipate energy under the gutter downspout. Possible options include splash pads/blocks, gravel, rock or adequate vegetation. Driveways Scenario 1: Paved Driveway: Flows into right-of-way (roadside drainage or street) No additional treatment necessary at this time. Homeowners will be notified when the TRPA develops an alternate approach to managing driveway runoff in areas with slowly infiltrating or seasonally wet soils. Scenario 2: Paved Driveway: Flows back onto property If driveway runoff flows onto the property, armor the area where water is exiting the paved surface with a 3-inch layer of drain rock, cobble, or riprap. This armoring should be a minimum of 2 feet wide to adequately capture and infiltrate the runoff from the driveway. Before applying drain rock, it is important to break up compacted soil with a hard rake or shovel to increase soil permeability. If the runoff is dispersed onto an area with established vegetation and there are no signs of erosion, this may be an acceptable BMP treatment. Scenario 3: Unpaved Driveway Driving on unpaved surfaces compacts the soil making it nearly impermeable. Because stormwater cannot infiltrate into this compacted area, it can leave the property carrying contaminates and sediment into the local waterways. For these reasons, all property owners are required to pave approved roads, driveways, and parking areas. Currently, it is not necessary to install driveway conveyance and infiltration systems when paving the driveway because site characteristics prohibit stormwater capture and infiltration in this area. Grading considerations can make a difference in implementing appropriate source control measures. One option may be to slope the driveway to one side so that all runoff flows into a rock armored or well vegetated area. Any area of the property that has been compacted due to vehicular traffic needs to be either paved or restored to a point that it can sustain vegetation. Refer to the online resource Paving Residential Dirt Driveway (http://tahoercd.org/publications-links/bmp-driveway-resources/) and Standard Drawing BMP-026.1 and the General Landscaping/Soil Areas section earlier in this document for more information. It is advisable to document existing conditions before making any changes to the property to avoid losing existing coverage rights. For information on land capability and coverage, please visit www.trpa.org. Paving Options Contact the Building Department for paving and/or encroachment permit information. Encroachment permits can only be issued to a licensed contractor. The minimum: paving two parking spaces within the property boundary
The standard paving permit will allow you to pave the minimum amount of off-street parking required by your local jurisdiction. This is usually two off-street parking spaces, approximately 400 square feet. A paving permit is not a verification of existing coverage or use. If you want to verify coverage a site assessment is necessary. For more information on land capability/land coverage visit http://www.trpa.org. Paving more than the minimum It is advisable to complete the site assessment process if paving more than the minimum to avoid potential loss of rights to existing coverage. In some instances a site assessment may be required in order to receive a paving permit. For more information on land capability/land coverage, visit http://www.trpa.org. Larger driveway installations that involve the grading of more than 3 to 7 cubic yards of soil may require a grading permit. Refer to the Paving Residential Dirt Driveways document available at http://tahoercd.org/publications-links/bmp-driveway-resources/ for more information. Storage Areas Install appropriate BMP for storage area Storage areas are those used for long term storage of vehicles, trailers, boats, snow or any other materials that are seldom moved off of the property, resulting in minimal soil erosion and compaction. Mulching is one of the simplest and most beneficial conservation practices a homeowner can use for erosion control. Mulching protects the soil from erosion and reduces compaction from the impact of heavy rain and material storage. Possible mulches include woodchips, redwood or cedar bark, drain rock, and cobble (3”-10” diameter rock). Apply chosen mulch material at a uniform 3” depth. Restore all compacted bare soil areas If there are any areas that are not treated with the methods mentioned above, cover soil with 2 inches of compost and till to a depth of 6 to 8 inches and plant, seed, and/or till in 2-3 inches or wood chip or tub grindings to depth of 6-12 inches. A combination of native or adapted vegetation and mulch produces a low maintenance landscape that is highly effective at preventing erosion. Learn more by reading the Common Ground document available at http://www.trpa.org/documents/press_room/2012/BMP_DSBrochure.pdf. There are many native and adapted grasses, plants, shrubs, and trees that can be used. Please review the recommended plant list in chapter 7 of the Home Landscaping Guide to help identify species to suit individual property and landscaping goals. In order to prevent future soil degradation, parking barriers can be installed to restrict vehicular access to restored areas. Parking barriers can be made from a variety of materials such as split rail fencing, boulders, wood posts, or shrubs. Refer to Lake Tahoe Standard Drawing BMP-026. Upon request, the Tahoe RCD can provide additional restoration guidance. Refer to the Living with Fire- Lake Tahoe Basin guidelines or contact the local fire district for acceptable organic mulching materials and methods. It is advisable to document existing conditions before making any changes to the property to avoid losing existing coverage rights. For information on land capability/land coverage please visit www.trpa.org. Decks / Stairs / Walkways Homeowners are responsible for stabilizing bare soil under elevated structures and/or around the perimeter of low elevated structures. To protect the soil under these structures from water and wind erosion, refer to the relevant treatment descriptions listed below. All deck treatments require borders to contain the drain rock and exclude adjacent soil.
Install drain rock under elevated structure (decks, stairs, and walkways) and border system; Refer to Lake Tahoe Standard Drawing BMP-010 Install a 3-inch layer of drain rock, cobble or rip rap under the entire footprint of the elevated structure and extend one foot past the edges to protect the soil in this area from water and wind erosion. Border the treatment to retain the rock and exclude adjacent soil. In the case that established, low growing, irrigated vegetation, such as lawn or dense vegetative cover exists underneath and around the perimeter of the low elevated structure; the vegetation will function as the BMP. To calculate drain rock quantities required, use the following formula: (Length in feet x Width in feet x Depth in feet)/27 = Cubic Yards. Install drain rock around perimeter of low elevated structure (decks, stairs, and walkways) and border system; Refer to Lake Tahoe Standard Drawing BMP-011 for installation instructions Install a 3-inch layer of drain rock or cobble around the perimeter of the low elevated structure and as far as is accessible underneath the structure. Extend one foot past the edges. Border the treatment to retain the rock and exclude adjacent soil. In the case that established, low growing, irrigated vegetation, such as lawn or dense vegetative cover exists underneath and/or around the perimeter of the low elevated structure, the vegetation will function as the BMP. To calculate drain rock quantities required, use the following formula: (Length in feet x Width in feet x Depth in feet)/27 = Cubic Yards. Install drain rock around perimeter of enclosed deck and border system Install a one foot wide, 3” layer of drain rock or cobble around the perimeter of the enclosed deck. Border the outside edges of the rock armor to retain the material and exclude adjacent soil. In the case that established, low growing, irrigated vegetation, such as lawn or dense vegetative cover, exists around the perimeter of the low elevated structure, the vegetation will function as the BMP. To calculate drain rock quantities required, use the following formula: (Length in feet x Width in feet x Depth in feet)/27 = Cubic Yards. Install rock slope protection (riprap) under elevated structure on steep slopes; Refer to online resource Lake Tahoe Standard Drawing BMP- 010, 040, 041 Install rock slope protection (riprap) under the elevated structure to dissipate runoff velocity and prevent erosion. Rock slope protection works best when integrated with a layer of filter fabric or other permeable weed blocking materials. Refer to pages 16 - 19 of the Home Landscaping Guide for more information on slope stabilization practices. Install armor treatment adjacent to patio/walkway and border system; Refer to Lake Tahoe Standard Drawing BMP- 006, 007 Armor the area where water is exiting the impermeable surface with a 3-inch layer of drain rock, cobble, or riprap. This armoring should be a minimum of one foot wide to adequately capture and infiltrate the runoff from the impermeable surface. Before applying drain rock, it is important to break up compacted soil with a hard rake or shovel to increase soil permeability. If the runoff is dispersed onto an area with established vegetation and there are no signs of erosion, this may be an acceptable BMP treatment. Slope Stabilization If steep slopes exist on the property, it is important to stabilize them to prevent potential movement of sediment into the local waterways and eventually into Lake Tahoe. A variety of options are available to homeowners who have eroding slopes on their properties. While gentler slopes may be stabilized with vegetation, mulch, and/or erosion control blankets, steep slopes may require the use of riprap, terracing, or retaining walls. Refer to pages 16 - 19 of the Home Landscaping Guide for more information on slope stabilization practices.
Install rock slope protection (riprap), terracing, and/or appropriate vegetation and mulch to stabilize slope; Refer to online resource Lake Tahoe Standard Drawing BMP-040, 041, 042, 043 Gentle slopes can be stabilized with vegetation, mulch, and/or erosion control blankets. Steeper slopes may require the use of terracing, riprap, or retaining walls constructed from boulders, rocks, concrete blocks, or wood products. Large projects and walls higher than 4 feet (measured from the bottom of the footing to the top of the wall) require professional engineering expertise and building permits. If manufactured products are used, follow the manufacturer’s specifications for proper installation. Refer to pages 16 - 19 of the Home Landscaping Guide for more information on slope stabilization. Install rock slope protection (riprap) Riprap (larger angular rock material) may be used to stabilize steep slopes. It is a good practice to spread native or adapted seed on the slope prior to rock placement. Rock slope protection works best when integrated with vegetation. Install retaining walls or terracing Retaining walls and terraces are a good way to stabilize steep eroding slopes. Common building materials include boulders, rocks, concrete blocks, or wood products. A building permit is required for the construction of retaining walls that are over 4 feet in height measured from the bottom of the footing to the top of the wall. Large projects and walls higher than 4 feet require professional engineering expertise. If manufactured products are used, follow the manufacturer’s specifications for proper installation. When installing retaining walls or terraces, please contact the local building service department to verify building codes.
Erosion Control under Elevated Deck
Erosion Control at Perimeter of Low Deck
Typical BMP Treatments use appropriate material in the 5-foot noncombustible zone
Roof Runoff falls to Turf
Roof Runoff falls to Rock Armor
Roof Runoff falls to Vegetated Bed
Roof Runoff flows to Energy Dissipater under Gutter
Downspout
Sloped Driveway Conveys Runoff to Rock Armor
Sheet Flow
Slope Stabilized with Retaining Wall, Rock
and Vegetation
Street
Example BMP Retrofit Site PlanLake Tahoe, CA
Tahoe Resource Conservation District
Designed
Checked
Approved
Date
Date
Date
turf or vegetated
groundcover
Drain Rock Armor
Impervious Surface/
Structure Outline
Impervious Surface Flow
Recommended Treatment
LEGEND
A
this Example bmp Site Plan is for the design and installation of Best Management Practices only. it is not a verification of land coverage, land capability, units of use, or other development capacities regulated by
the tahoe regional planning agency (trpa) nor is it a conceptual approval of any unrelated future project. these verifications require the submittal of a separate application to the trpa for review and approval.
bmp treatments must be installed within the property boundary lines. any reference to a property boundary line is an approximation. before any installation confirm property boundary lines.
Tahoe RCD 07/17/2013
A
B
C
DDeck
Property Line
Typical Source Control Treatments
Soil Areas: Maintain existing vegetation; Vegetate and/or
mulch to restore and stabilize (In accordance with "living
with fire" guidelines and the Home Landscaping Guide for Lake
Tahoe and Vacinity); protect restored soil areas with parking
barriers as needed (see BMP−003 Lake Tahoe Standard Drawing).
placement of systems is dependent upon specific site
characteristics. Diagram shows relation and location of components.
Roof runoff: Install armored Drip Line With border (see BMP−009
Lake Tahoe Standard Drawing).
Driveways: armor runoff reciveing area where water flow back onto
property (see BMP−024 Lake Tahoe Standard Drawing).
Decks: erosion control for elevated and low elevated structures
(see BMP−010 and BMP−011 Lake Tahoe Standard Drawings).
Stabilize eroding slopes(see BMP−040, BMP−041, BMP−042, BMP−043,
and the Home Landscaping Guide for Lake Tahoe and Vacinity.
B
B
E slope
retaining
wall
parking barriers
Roof
Valley
Well Maintained
Lawn
A
B
C
D
E
BMP Final Inspection Checklist
2/11 Rev.
APN ____________________ Site Address __________________________________ County ______________
Inspector ________________________ Agency ____________ Date ___/___/___
This form assists inspectors to assess whether Best Management Practice (BMP) treatments are complete and functioning. Previous Tahoe Regional Planning Agency and Resource Conservation District Site Evaluations will be considered in recommendations for pass/fail determinations. “Yes” answers indicate correct BMP installation. “No” answers indicate a missing or incorrect BMP installation. “N/A” answers indicate that the question does not apply to the property. Any property that passes final inspection with a “No” must have an explanation in the comments section. If the property does not pass a final inspection, evaluators shall document any necessary corrective steps in the comments section. Date of Site Evaluation ___/___/___ Evaluator___________________________ Agency____________ BMP Treatments designed by: \ RCD Contractor/Consultant Property Owner Other: _________________________
Open Space, Yard and Landscape Areas Yes N/A No
2. Have compacted bare soil areas been aerated (tilled or ripped), vegetated and/or mulched, and, if appropriate, blocked from vehicular access? Comments:
1. Have all visual signs of erosion (eroding slopes, rills, gullies, unstable flow channels, etc.) been addressed through appropriate stabilization methods (vegetation, mulch, terraces, retaining walls, riprap, or other appropriate method)? Comments:
Yes N/A NoDriveways
4. Was a water test conducted (for at least 10 minutes with a hose) to verify runoff conveyance and infiltration systems are connected and functioning? Comments:
3. Are driveways paved with runoff conveyance and infiltration systems Installed and, if required or applicable, are infiltration systems installed with containment borders, filter fabric, and a sediment trap? Comments:
Storage Areas Yes N/A No
5. Are storage areas (boats, trailers, snow, automobiles, etc.) stabilized with appropriate vegetation and/or mulch? Comments:
Yes N/A No Roof Drip Lines and Decks
6. Is all stormwater runoff from roof drip lines mitigated by an appropriate treatment system (rock, prefabricated, or vegetated systems with containment borders where applicable)? When applicable, are the associated conveyance systems such as gutters and downspouts functional? Comments:
7. Is the soil under decks, walkways, and elevated structures adequately protected from erosion with appropriate BMPs? Are containment borders included around drain rock treatments? Comments:
Yes NoBMP Maintenance
8. Are all BMPs maintained and functioning correctly (conveyance and infiltration systems, soil and slope stabilizations, etc.)? Comments:
Installation Verification
9. What type of documentation was provided to or by the inspector to verify proper installation? Photos Calculations Approved Site Evaluation Approved Design Changes Comments:
Certification
IS THE PROPERTY ELIGIBLE FOR A BMP CERTIFICATE OF COMPLETION? Comments:
Yes No
IS THE PROPERTY ELIGIBLE FOR A BMP SOURCE CONTROL CERTIFICATE? Comments:
roof drip
line
roof valley drip line treatmentconstruction notesThis detail applies to roof drip lines that require additional
armor to protect the soil where roof valleys concentrate
flow and project runoff beyond the standard width trench
or drain rock armor treatment.
Refer to applicable standard drawings, BMP−001, "Drip Line
Infiltration Trench," or BMP−009, "Armored Drip Line,"
for more detail.
"W" is the width of the Drip line treatment as defined in
the BMP "Site Evaluation Recommended Treatments" form.
When estimating the quantity of drain rock required, account
for the area beyond the standard width treatment with a 3"
minimum layer of 3/4" to 1 1/2" drain rock. Otherwise, use
appropriate depth to estimate quantity of larger rock
material such as riprap.
1.
2.
3.
2W
2W
W
4.
LEGEND
Impervious Surface/
Structure Outline
roof valley
impervious surface flow
drain rock
U.S. Department of AgricultureNatural Resources Conservation Service
Tahoe Resource Conservation DistrictNevada Tahoe Conservation District Drawn By: Approved By:
in cooperation with
Date
, and
2W
W
2W
6"
6"
W
roof
valley
BMP−002
W
W
2W
2W
DMGG/MPB
USDA is an equal opportunity provider and employer
This Standard Drawing is based on a reference to the NRCS standard practice 570 − Stormwater Runoff Control. This drawing is intended to assist the
designer in preparation of a complete site specific design, and it is not to replace the independent judgment and analysis by a qualified designer.
standard drawing no.
date: 4−6−2012
(residential use only)
best management practicelake tahoe
standard
drawing
1.
2.
3.
4.
5.
6.
armored drip lineconstruction notes
Unless specified otherwise, the minimum trench widths shown in
the installation guidelines reflect the minimum requirements
for the BMP retrofit ordinance. See BMP−002 for details of
trenches located under roof valleys.
Armor soil with a 3" minimum continuous layer of rock. Washed
3/4" to 1 1/2" drain rock or cobble is recommended. Native
rock can be substituted if available.
On sloped drip lines over 10%, contain the drain rock with
baffles as shown or substitute larger riprap for drain rock.
An alternative practice is to construct a swale or
subsurface drain to collect and convey runoff to an
infiltration system located a minimum of 10’ away from the
foundation. See BMP−004 and BMP−005 for details.
Containment borders are required. Options for materials
include pressure treated lumber, recycled composites,
brick, stone, cobble, or other landscape edging material.
Fire Defensible Space Guidelines for Lake Tahoe recommend
a non−combustible area within 5 feet of a structure.
Combustible material shall not connect from the border to
the structure.
Consult with your local fire protection district when
landscaping near structures. Visit www.livingwithfire.info/tahoe
for guidelines on the defensible space zone.
Regularly scheduled maintenance is necessary to maintain full function. Maintenance includes inspection, removal, and proper disposal of pine needles and accumulated sediment.
BMP−009
drip line
baffle
drip line
installation guidelinessee note 5
see note 5
6" min. finish
grade to bottom
of siding
border − see note 4
sub−grade shall slope 2% minimum
away from foundation for 5’
drain rock
3" depth
see note 5
6" min.
containment
border
1 story = 18"
2 story = 24"
3 story = 30"
slope
5’1015
slope
%
baffle
spacing on
rock armor
N/A 0−1010’
min. trench width
L
W
in cooperation with Nevada Tahoe Conservation District
Tahoe Resource Conservation DistrictDrawn By: Approved By: Date
DMGG/MPB
, and
US Department of Agriculture
Natural Resources Conservation Service
USDA is an equal opportunity provider and employer
This Standard Drawing is based on a reference to the NRCS standard practice 570 − Stormwater Runoff Control. This drawing is intended
to assist the designer in preparation of a complete site specific design, and it is not to replace the independent judgment and analysis by a qualified designer.
standard drawing no.
date: 4−6−2012
(residential use only)
best management practicelake tahoe
standard
drawing
2.
Sub−grade shall slope 2% minimum away from foundation for 5’.
Place rock armor below the entire elevated structure footprint
and extend 12" out from the perimeter. Inaccessibility may limit
treatment under entire footprint.
3/4" to 1 1/2" drain rock or cobble is recommended for rock armor
on slopes between 0 and 15%. Install baffles as shown to
contain rock on slopes between 10% and 15%. Native rock can be
substituted if available. Use Rock Slope Protection on
steeper slopes. See BMP−040 and BMP−041 for detail.
Finish grade of rock shall be at least 6" below wood siding to
maintain earth to wood separation required by local building
codes.
Containment borders are required. options for materials include
pressure treated lumber, recycled composites, brick, stone,
cobble, or other landscape edging material. Fire Defensible
Space Guidelines for Lake Tahoe recommend a non−combustible
area within 5 feet of a structure. Combustible material shall
not connect from the border to the structure.
Consult with your local fire protection district when landscaping
near structures. Visit www.livingwithfire.info/tahoe for guidelines
on the defensible space zone.
Remove pine needles and accumulated sediment to maintain full function. keep area clear of stored materials such as firewood, lumber, household items, etc.
erosion control for elevated structures
construction notes
installation guidelines
containment
border
rock armor
3" layer min.
elevated deck
elevated stairs
containment border
12" min.
all sides
(Decks, open staircases, walkways, and elevated driveways)
U.S. Department of AgricultureNatural Resources Conservation Service
Tahoe Resource Conservation DistrictNevada Tahoe Conservation District Drawn By:
DMGG/CLT
Approved By:
in cooperation with
Date
, and
min.distance from finish
grade to bottom of siding
6"
min.
deckroof
baffles
see note 6
see note 6
baffle spacing
for rock armorslope %
N/A
5’10’
0−101015
7.
6.
5.
4.
3.
1.
see note 5
BMP−010
rock armor
This Standard Drawing is based on a reference to the NRCS standard practice 570 − Stormwater Runoff Control. This drawing is intended to assist the
designer in preparation of a complete site specific design, and it is not to replace the independent judgment and analysis by a qualified designer.
USDA is an equal opportunity provider and employer
standard drawing no.
date: 4−6−2012
(residential use only)
best management practicelake tahoe
standard
drawing
construction notes
installation guidelines
containment border
elevated deck
see note 6
distance drain rock is placed back
underneath deck− see note 2
drain rock 3" layer
inaccessible area
containment border
distance "X" depends
on accessibility,
12" minimum
drain rock 3" layer
X
X
12"U.S. Department of Agriculture
Natural Resources Conservation Servicein cooperation with
Tahoe Resource Conservation District , and
Nevada Tahoe Conservation District Approved By: DateDrawn By:
DMGG
min.
see note 5
BMP−011
1.
2.
3.
4.
5.
6.
7.
Sub−grade shall slope 2% minimum away from foundation for 5’.
Place rock armor as far back under the low elevated structure
as possible. Inaccessibility may limit treatment under the entire
footprint. Extend rock armor 12" out from the perimeter of the
structure.
3/4" to 1 1/2" drain rock or cobble is recommended for rock armor.
Native rock can be substituted if available. Use rip rap on
steeper slopes.
Finish grade of drain rock shall be at least 6" below wood
siding to maintain wood and earth separation required by
local building codes.
Containment borders are required. options for materials include
pressure treated lumber, redwood, recycled composites, brick,
stone, cobble, or other landscape edging material. Fire
Defensible Space Guidelines for Lake Tahoe recommend a
non−combustible area within 5 feet of a structure. Combustible
material shall not connect from the border to the structure.
Consult with your local fire protection district when
landscaping near structures. Visit www.livingwithfire.info/tahoe
for guidelines on the defensible space zone.
Remove pine needles and accumulated sediment to maintain full function. keep area clear of stored materials such as firewood, lumber, household items, etc.
for low elevated structures erosion control
This Standard Drawing is based on a reference to the NRCS standard practice 570 − Stormwater Runoff Control. This drawing is intended to assist the
designer in preparation of a complete site specific design, and it is not to replace the independent judgment and analysis by a qualified designer.
USDA is an equal opportunity provider and employer
standard drawing no.
date: 4−6−2012
(residential use only)best management practicelake tahoe
standard
drawing
driveway edge armorconstruction notes
installation guidelines
elevation drop (1/2" minimum)
border drain rock or
cobble
driveway
W
flow
curb
pavement in
right−of−way
vegetation
and/or mulch
driveway
elevation
drop
drain rock
(3" depth)
borderThis practice applies to driveways that do not require a
conveyance to capture runoff. The driveway must uniformly
slope 2% min. toward the side and water cannot leave the
site. See BMP−003 for details on alternative practices
that capture, convey and treat runoff.
Refer to the BMP "Site Evaluation Recommended
Treatments" form for site specific BMP dimensions and
associated natural infiltration treatment area that
applies to your site.
Border next to driveway must be placed lower than
driveway surface elevation to allow runoff to enter
system evenly.
Armor soil with a 3" minimum continuous layer of rock.
Washed 3/4" to 1 1/2" drain rock or cobble is recommended.
Native rock can supplement drain rock or be substituted if
available.
Containment borders are required. Options for materials
include pressure treated lumber, recycled composites, brick,
stone, cobble, or other landscape edging material. Fire
defensible Space Guidelines for Lake Tahoe recommend a
non−combustible area within 5 feet of a structure.
Combustible material shall not connect from the border to
the structure.
Regularly scheduled maintenance is necessary to maintain full function. Maintenance includes inspection, removal, and proper disposal of debris, pine needles and accumulated sediment.
1.
2.
3.
4.
5.
6.
W
L
USDA is an equal opportunity provider and employer
aggregate base
sub−base
BMP−024
This Standard Drawing is based on a reference to the NRCS standard practice 570 − Stormwater Runoff Control.
This drawing is intended to assist the designer in preparation of a complete site specific design, and it is not to replace the independent judgment and analysis
by a qualified designer. Infiltration system sizing is calculated based on the hydraulic conductivity of the soils on site and volume of runoff being captured.
natural infiltration
area, see note 2
U.S. Department of AgricultureNatural Resources Conservation Service
Drawn By:
DMGG/MPB
Approved By: Date
Tahoe Resource Conservation Districtin cooperation with
Nevada Tahoe Conservation District , and
property line
flow
standard drawing no.
date: 4−6−2012
(residential use only)
best management practicelake tahoe
standard
drawing
3"
parking barriers
construction notes
typical parking barriers
parking barriers
vegetation and
organic mulch
boulders
wood posts
fencing
shrubs or well
established
vegetation
Parking barriers shall be placed to restrict
vehicular access on disturbed soil areas.
boulders:
boulders shall be greater than 18" diameter and
be keyed in to the soil a minimum of 6"
posts:
wood posts shall be a minimum of 2’ above grade,
and anchored in a concrete footing
shrubs or well established vegetation:
this parking barrier is not recommended in areas
used for snow storage
fencing
posts shall be anchored in a concrete footing
Information on rehabilitating disturbed soil
areas can be found on the NRCS "direct seeding
of disturbed areas" tip sheet.
Regularly scheduled maintenance including service, repair, or replacement of components is necessary to maintain full function.
1.
2.
3.
This Standard Drawing is based on a reference to the NRCS standard practice 561 − Heavy Use Area Protection Systems.
This drawing is intended to assist the designer in preparation of a complete site specific design, and it is not to replace the independent judgment and analysis by a qualified designer.
U.S. Department of AgricultureNatural Resources Conservation Service
in cooperation with
Tahoe Resource Conservation District , and
Nevada Tahoe Conservation District Approved By: DateDrawn By:
SKB
BMP−026
USDA is an equal opportunity provider and employer
standard drawing no.
date: 4−6−2012
(residential use only)
best management practicelake tahoe
standard
drawing
Materials Calculatorin Cubic Yards
For calculating drain rock quantities at a 3" depth
Linear Feet 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20
18 inches 0.1 0.1 0.1 0.1 0.1 0.1 0.2 0.2 0.2 0.2 0.2 0.2 0.2 0.3 0.3 0.3
24 inches 0.1 0.1 0.1 0.1 0.2 0.2 0.2 0.2 0.2 0.3 0.3 0.3 0.3 0.3 0.4 0.4
30 inches 0.1 0.1 0.2 0.2 0.2 0.2 0.3 0.3 0.3 0.3 0.3 0.4 0.4 0.4 0.4 0.5
60(5 feet) inches 0.2 0.3 0.3 0.4 0.4 0.5 0.5 0.6 0.6 0.6 0.7 0.7 0.8 0.8 0.9 0.9
Linear Feet 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36
18 inches 0.3 0.3 0.3 0.3 0.3 0.4 0.4 0.4 0.4 0.4 0.4 0.4 0.5 0.5 0.5 0.5
24 inches 0.4 0.4 0.4 0.4 0.5 0.5 0.5 0.5 0.5 0.6 0.6 0.6 0.6 0.6 0.6 0.7
30 inches 0.5 0.5 0.5 0.6 0.6 0.6 0.6 0.6 0.7 0.7 0.7 0.7 0.8 0.8 0.8 0.8
60(5 feet) inches 1.0 1.0 1.1 1.1 1.2 1.2 1.3 1.3 1.3 1.4 1.4 1.5 1.5 1.6 1.6 1.7
Linear Feet 37 38 39 40 41 42 43 44 45 46 47 48 49 50
18 inches 0.5 0.5 0.5 0.6 0.6 0.6 0.6 0.6 0.6 0.6 0.7 0.7 0.7 0.7
24 inches 0.7 0.7 0.7 0.7 0.8 0.8 0.8 0.8 0.8 0.9 0.9 0.9 0.9 0.9
30 inches 0.9 0.9 0.9 0.9 0.9 1.0 1.0 1.0 1.0 1.1 1.1 1.1 1.1 1.2
60(5 feet) inches 1.7 1.8 1.8 1.9 1.9 1.9 2.0 2.0 2.1 2.1 2.2 2.2 2.3 2.3
Use this calculation sheet to determine minimum BMP drip line treatments or to determine the amount of drain rock needed for rock armoring in the five-foot non-combustible area. Measure the length of the eaves for drip line calculations or along the foundation or footings of building structures for fire defensible space calculations. When adding linear feet for fire defensible space, subtract 5 feet from inside corners and add 5 feet to outside corners of structures. Find this length on the calculation sheet and coordinate it with the width criteria. Drip line treatments must extend a minimum of 6” inside and 12” beyond the drip line of a single story roof (18” total), 18” of a two-story roof (24” total), and 24” of a three-story roof (30” total). Local fire defensible space requirements include a five-foot non-combustible soil surface treatment, such as turf or rock, around the perimeter of building structures.
Wid
th o
f tre
atm
ent
Wid
th o
f tre
atm
ent
Wid
th o
f tre
atm
ent
(Length in Feet x Width in Feet x Depth in Feet) / 27 = Cubic Yards
TRCD / NRCS 870 Emerald Bay Road
Suite 108 South Lake Tahoe, CA 96150 Phone: 530-543-1501 x 113
Fax: 530-543-1660
The Tahoe Resource Conservation District asks for your assistance in helping us to continue keeping our services free of charge to landowners like you. We are asking you to allow us to release your BMP Retrofit Site Evaluation to our funding agencies. Once you have signed below please return either by fax (530-543-1660) or mail (870 Emerald Bay Rd, Suite #108 SLT, CA 96150).
PRIVACY POLICY for the Backyard Conservation and BMP Retrofit Program
The information provided to and complied by the Tahoe Resource Conservation District, in partnership with USDA is confidential until the landowner allows for its release*. This policy is followed for all work completed by the District, including Best Management Practices (BMP) Retrofit site evaluations.
WHAT BENEFITS ARE THERE TO RELEASING MY BMP SITE EVALUATION PLANNING INFORMATION?
If you allow the District to release your BMP site evaluation, we will be able to work with you from design to certification. The District has been given the authority by the Tahoe Regional Planning Agency (TRPA) to complete Certificate of Completion inspections for landowners that we have worked with. Also, if you authorize the release of your BMP site evaluation, it will be posted on a web-based database that may be viewed by you, or your agent (realtor, contractor, or your designated property manager). This may help you to transfer documents quickly in order to complete real estate transactions, or to communicate quickly with a number of contractors to obtain bids.
If you do not release this information, be advised that once you have installed your BMPs as prescribed in your site evaluation to improve water quality, the Tahoe Regional Planning Agency will require that you release the ‘Site Evaluation’ to them, in order for them to accept your installation and send you a Certificate of Completion showing that you have met their Ordinance requirements.
AUTHORIZATION TO RELEASE BMP SITE EVALUATION INFORMATION
I hereby give authorization to the Tahoe Resource Conservation District to release my BMP site evaluation information to any person who requests it. I understand that upon this release the BMP information becomes a matter of public record and is accessible to anyone who requests that information under the California Public Records Act. X . Printed Name ______________________________ DATE ____________________ Property Address Mailing Address Telephone # home: _________________________ mobile: ____________________________ * Confidentiality based on rights outlined in the Privacy Act of 1974 and the protection of my personal
information under USDA, NRCS General Manual Part 408.
USDA is an equal opportunity provider and employer.
©Thriftyfun.c
Yard
Fertility
Management
USDA, Natural Resources Conservation Service
What is Yard Fertility Management?
Fertility Management in your yard and garden means maintaining a
healthy plant and soil environment by supplying the right amount of
nutrition, in the right place, at the right time.
Plant Nutrition
Twenty nutrients have been identified that are required by plants.
Of these, nitrogen, phosphorus, and potassium are required in
relatively large amounts. Nitrogen stimulates vegetative growth,
phosphorus encourages flowering and fruiting, and potassium helps
a plant resist stress and disease.
Calcium, sulfur, and magnesium are also required in comparatively
large quantities. These six nutrients are referred to as
macronutrients. The other nutrients, referred to as micronutrients,
are required in very small amounts. These include such elements as
copper, zinc, iron, and boron. While both macro and
micronutrients are required for good plant growth, over-
application can be as detrimental as a deficiency. Over-application
of plant nutrients not only may impair plant growth and increase
it’s susceptibility to pest but may contaminate groundwater by
leaching through the soil or pollute surface waters by washing
away.
Fertilizers and Soil Amendments
All fertility supplements, both natural and chemical, have the
potential to impair water quality if used in excessive amounts. You
can eliminate or minimize your dependence on fertilizer by
landscaping with the many beautiful native and adapted grasses,
shrubs, and trees that have little need for fertility supplements.
When fertility supplements are necessary, consider alternatives to
chemical fertilizers such as compost and mulching of lawn clippings.
Organic soil amendments are easy to use, safer for the
environment and the gardener, and can save you time and money!
Fertilizing With Compost
Compost supplies essential plant nutrients, including micro
nutrients not found in most mineral and chemical fertilizers, and is
especially beneficial in improving the condition of the soil. By
keeping the soil loose, compost allows plant roots to grow well
throughout the soil, allowing them to extract nutrients from a
larger area. A loose soil enriched with compost is an excellent
habitat for earthworms and other beneficial soil microorganisms
that are essential for releasing nutrients for plant use. Fertilizing
with compost adds organic material to the soil which increases the
soil’s water holding capacity and reduces the need for frequent
watering. The nutrients from mature or stable compost are also
released slowly so there is little concern for "burning" the plant
with an over-application.
If preparing a bed before planting, compost may be worked into the
soil to a depth of 6 to 12 inches. If adding to existing plants,
carefully work the compost into the upper 2 to 3 inches of soil
around the base of the plants.
Compost can also be applied to a lawn: Using high quality fine
textured compost apply a thin layer (less than ¼ inch) to the lawn
and spread with a rake. When compost is distributed evenly, water
for 15 to 20 minutes. After this, water your lawn as you normally
would but allow seven to eight days before mowing.
Mulching of lawn clippings
Leaving grass clippings on the lawn, when done properly, provides
many benefits including:
� Shading the surface of the soil which helps prevent
moisture loss
� Help decompose thatch
� Saves time and energy from raking and reduces
waste sent to landfill.
� Can provide up to 2 lbs (a years worth) of
Nitrogen annually!
� Provides Phosphorus and Potassium
Lawn clippings are very high in nitrogen and clippings less than one
inch in length break down rapidly and actually help decompose
thatch. A good rule of thumb is to mow when your grass is dry and
3 to 3-1/2 inches tall. Never cut it shorter than 2 to 2-1/2 inches or
remove more than one third of the leaf surface at any one mowing.
If you must mow when the grass is wet or remove more than one
inch, clippings should be removed and composted. See the
Backyard Conservation tip sheet for Yard Waste Composting.
Mineral and Synthetic Fertilizer
If mineral or synthetic fertilizer is selected for use, its application
should be tailored to the needs of the plants and the soils in your
area. Over application of phosphorus is a concern for Tahoe soils.
Phosphorus is a highly mobile nutrient and can easily be leached
out of our coarse textured soils or carried by runoff into
waterways causing algae blooms. Therefore fertilizers with little to
no phosphorus are recommended for the Lake Tahoe Basin. Too
much fertilizer or fertilizer applied when the plant is not actively
growing will move beyond the root zone before it can be used,
resulting in wasted money and potential pollution.
Mineral and Synthetic Fertilizers are available in many different
formulations. All fertilizers will be labeled with a “guaranteed
analysis” which shows the percentage of nitrogen, phosphorus, and
potassium. A formulation recommended for Tahoe soils is 27-0-12.
This fertilizer contains 27% N, 0% P, and 12% K.
Be sure to choose the right fertilizer formulation for your needs.
Plants differ in their nutritional needs and a fertilizer developed for
vegetables will not be appropriate for lawns or shrubs. For
chemical fertilizer use, pelletized slow release fertilizers are the
best choice for most lawn and garden situations.
When fertilizing lawns in the early summer and late summer, apply
only 1/2 to 3/4 pound of actual nitrogen per 1000 square feet of
lawn on each application (maximum of 2 applications per year).
Timing
For the most efficient use and to decrease the potential for
pollution, fertilizer should be applied when the plants have the
greatest need for the nutrients. Plants that are not actively growing
do not have a high requirement for nutrients. Therefore,
applications of nutrients to dormant plants, or plants growing
slowly due to cool temperatures, are more likely to be wasted.
Late season applications of nitrogen fertilizers are not recommend
for the cold climate of the Lake Tahoe Basin. Since nitrogen
encourages vegetative growth, if it is applied in the fall it may
reduce the plant's ability to harden properly for winter and leave
the plant more susceptible to early frosts.
Safe and Effective Fertility Management
� Choose the right fertility amendment for your needs and
apply in the right amount at the right time.
� Sweep up any fertility amendment spilled on hard
surfaces and reapply to the grass or garden area.
� Do not use any fertilizer within 25 feet of a stream
or riparian area.
� Never apply fertilizers to frozen ground or snow.
� Leave a natural filter strip of grass, trees, and/or shrubs
next to the shoreline.
� Do not over water! Too much water will leach nutrients
out of the root zone before they can be used. See our
Turf Water Management tip sheet for more information.
� When in doubt do not hesitate to contact your local
conservation district or the NRCS for additional advice.
For Further Information Contact:
In Nevada
Nevada Tahoe Conservation District
775-586-1610 x 28
In California
Tahoe Resource Conservation District
530-543-1501
Or
Natural Resources Conservation Service
530-543-1501
Sure-Gro Lawn
….Food
20 - 2 - 4 jfjpfp uwofjfofojfkkgkg
SureSureSureSure----GroGroGroGro Lawn Food
20 - 2 - 4
Guaranteed Analysis
Total Nitrogen (N)……..….20%10.4% Ammonium Nitrogen3.4% Urea Nitrogen3.7% other Nitrogen
Available Phosphoric Acid…..2%
Soluble Potash……………4%
Derived from Sulphur-coated ureaand Sulfate of AmmoniaNet Weight 10 lbsNet Weight 10 lbsNet Weight 10 lbsNet Weight 10 lbs
Product Brand Name
Name Manufacturers warrantyon the contents of the bag.
Base source of fertilizernutrients used in this product.
Formula percentages of nitrogen,phosphate, and potassium(always in that order). Since allthree nutrients are present,
this would be a“complete fertilizer”.
Fast release forms of nitrogen.
Nitrate nitrogen is also afast release form.
Slow release form of nitrogen.Also may be shown assulphur-coated Urea, IBDU,Ureaform resin-coated and Plastic coated nitrogen
Sample Fertilizer Label
Appendix F: Soil Infiltration Investigation Report
Soil Investigations on public lots within the project area:
In 2012 the NRCS, Tahoe RCD and the TBI joined together to investigate soil characteristics on selected public
lots within the city of South Lake Tahoe. The purpose of these investigations was to begin discussion about the
suitability of these undeveloped lots for installation of storm water treatment facilities such as infiltration
basins. Two main soil characteristics or attributes were examined to help determine suitability. These
attributes were Saturated Hydraulic Conductivity (Ksat) and depth to restrictive feature such as a high water
table or a fragipan.
The dominant soil series in the test area are Jabu, Christopher, and Marla. These soils are derived from glacial
outwash, are typically sandy loam in texture and gently sloping. The Jabu soils do have fragipans and high water
tables associated with the pan. Marla soils are wetter/shallower to a seasonal high water table but lack the
fragic properties of the Jabu series. Christopher soils are coarser in texture, lack the shallow water table and the
pan, and barring compaction tend to be the most permeable of the three. All three of these soil types, and the
soils in this area in general, tend to be susceptible to compaction, especially of disturbance happens when the
soils are moist.
A constant head permeameter (chp) was used to determine the ksat for each lot. The chp is simply a modified
Marriotte bottle that was designed for quick accurate assessment of Ksat in field situations. The reported Ksat
was determined by taking multiple test measurements at each lot. This was done to help account for the highly
variable nature of Ksat on a landscape. Testing depth was approximately 12 inches.
The depth to a seasonal high water table was determined by soil investigations using a bucket auger and
examining for redox features. The redox features are assumed to represent a seasonal high water table of
significance as redox features take time to develop. In other words, the redox features indicate that water was
at that level long enough for these features to form. This does not mean that there will be a water table at that
depth every year, but that in the past, there has been a water table there for some length of time.
The results revealed fairly consistent numbers in Ksat throughout the area. About 2 inches per hour was
common for these locations. The slowest sites measured approximately 1”/hour while the fastest site was over
of 11”/hr. Two inches/hour may seem like a low number, however, this is a reasonable number for most parts
of the county for things like septic design. Eleven inches/hour on the other hand, in some parts of the country,
would not be permitted to install septic systems due to their rapid permeability and perceived lack of filtration.
Fragipans and seasonal high water tables were observed on several of the lots. Frequently the depth of
observation was limited, large rocks within the soil profile for example. Therefore, fragipans and seasonal high
water tables may exist but below the observed depth.
Parcel Ownership CHP A CHP B CHP C CHP D CHP AVG
Fragipan inches
SHWT inches
Characteristic Vegetation Comments
1 CTC 0.4 1.5 3.6 2.0 1.9 32 Jeffery, Lodgepole, White fir, Mule's ear Weak pan
2 USFS 2.5 3.6 3.6 1.7 2.8 24 8
Jeffery, few Lodgepole, White fir, Mule's ear, grass, Scouler willows nearest to D
Pan measured at A/B, Redox measured at C/D. Slope down towards stream bed from A-D
3 CTC 2.5 6.0 4.3 Surface
Mule's ear, lodgepole, rose, incense cedar up slope, reed and rush down slope
CHP sites at upward part of slope. Don't trust site 3A reading!
4 CTC 4.5 3.0 2.5 3.0 3.3 Jeffery, Mule's ear Site A: originally water drained instantly, re-did this in new hole.
5 USFS 10.0 13.0 11.5 Same as Site 3 *Adjacent to site 3, only one soil sample for both sites
6 CTC 1.8 1.8 1.8 12 Jeffery, Lodgepole, White fir, Cinquefoil, Willow, Aspens, grass One soil sample for 6/7
7 CTC 1.7 2.2 1.9 Same as Site 6 Same as Site 6
8 CTC 2.9 3.0 0.8 0.7 1.9 36 Sage brush, bitter brush, grass, mule's ear, white fir, Jeffery Redox measured near site A
9 CTC 0.8 2.8 2.5 3.8 2.4 Jeffery, White fir, White thorn Slope, dry soil
10 CTC 5.0 0.2 0.8 4.0 2.5 29 Jeffery, White fir, Manzanita, White thorn
On top of hillside. Shallow Horizon A. C/D next to road.
11 CTC 4.0 4.5 1.6 0.8 2.7 Same as 10 Same as 10
Parcel Ownership CHP A CHP B CHP C CHP D CHP AVG
Fragipan inches
SHWT inches
Characteristic Vegetation Comments
12 CTC 4.8 1.5 2.6 0.3 2.3 18
13 CTC 0.1 1.0 2.5 2.0 1.4
Bare undrestory, Jeffery on half of site, Lupin, Arrow-leaf balsam root, Butter and eggs
Flat site. Soil very sandy and dry, potential fragipan/ hard pan just below O Horizon
14 CTC 0.8 4.8 1.4 0.7 1.9 36 Jeffery, Lodgepole, grass Flat, grassy. Additional measurement at A/B site: 1.75
15 CTC 2.3 3.5 1.3 2.0 2.3 27 Lodgepole, forbes and grasses, roses
16 USFS 1.0 1.1 1.1 Jeffery, Lodgepole, roses
17 USFS 3.5 2.1 2.8 27
Jeffery, few Lodgepole, rose bush, willow (may be planted), cheatgrass near Auger site
18 CTC 1.0 1.0 1.0 33 33 Jeffery, Fir, grass
19 CTC 3.5 2.8 3.2 18 Jeffery , Lodgepole, mule's ear, grass Adjacent to 18
20 CTC 1.3 1.9 0.1 3.6 1.7 36 36 Jeffery, bitter brush, grasses and forbes Weak pan
21 CTC 3.7 0.4 0.4 0.2 1.2 36 Jeffery, bitter brush, grasses Weak pan, compacted soil, low permeability. Flat
22 CTC 2.8 0.8 3.5 1.5 2.1 38
A/B: Jefferys, firs, rose and currents. C/D: grasses/forbes, vetch
Only 1 flag found (A/B). Sites C/D chosen based on difference in vegetation (more grasses/forbes and vetch vs. Jefferys, firs, rose and currents)
LOCATION CHRISTOPHER CA NV
Established Series
Rev: WRL/ET
05/2007
CHRISTOPHER SERIES
The Christopher series consists of very deep, somewhat excessively drained soils that formed in
glacial outwash derived from granodiorite. The Christopher soils are on glacial outwash terraces
in the tahoe basin. Slopes range from 0 to 30 percent. The mean annual precipitation is about 660
millimeters and the mean annual air temperature is about 5 degrees C.
TAXONOMIC CLASS: Mixed, frigid Dystric Xeropsamments
TYPICAL PEDON: Christopher Loamy coarse sand on a southeast facing (136 degree), 3
percent slope at an elevation of 1981 meters. When described on 08/09/2002 the soil was dry
throughout. Colors are for dry soils unless otherwise noted.
Oi--0 to 3 cm; Pine litter
A--3 to 20 cm; brown (10YR 5/3) loamy coarse sand, very dark grayish brown (10YR 3/2)
moist; 85 percent sand; 14 percent silt; 1 percent clay; weak fine subangular blocky structure;
soft, very friable, nonsticky, nonplastic; few very fine, fine and medium roots throughout; many
very fine interstitial pores; 9 percent gravel; moderately acid, pH 6.0; abrupt smooth boundary.
(8 to 25 cm thick)
Bw1--20 to 66 cm; yellowish brown (10YR 5/4) loamy coarse sand, brown (10YR 4/3) moist; 85
percent sand; 14 percent silt; 1 percent clay; weak fine subangular blocky structure; soft, very
friable, nonsticky, nonplastic; few fine and common medium and very coarse roots throughout;
many very fine interstitial pores; 2 percent cobbles 6 percent gravel; moderately acid, pH 5.7;
clear smooth boundary.
Bw2--66 to 107 cm; yellowish brown (10YR 5/4) loamy coarse sand, dark yellowish brown
(10YR 4/4) moist; 80 percent sand; 17 percent silt; 3 percent clay; moderate medium subangular
blocky structure; slightly hard, friable, nonsticky, nonplastic; few fine and medium roots
throughout; many very fine interstitial pores; 2 percent cobbles 7 percent gravel; moderately
acid, pH 5.9; clear wavy boundary.
Bw3--107 to 155 cm; yellowish brown (10YR 5/4) loamy coarse sand, dark yellowish brown
(10YR 4/4) moist; 80 percent sand; 18 percent silt; 2 percent clay; moderate fine subangular
blocky structure; soft, very friable, nonsticky, nonplastic; few fine, very fine and very coarse
roots throughout; many very fine interstitial pores; 9 percent gravel and 5 percent paracobbles;
slightly acid, pH 6.1 (the combined thickness of the Bw horizons is 76 to 191 cm thick)
TYPE LOCATION: El Dorado County, California, 2418 feet south and 1849 feet west of
Section 21, Township 12 N., Range 18 E., 38 degrees 52, minutes, 28.97 seconds north latitude
and 119 degrees, 59 minutes, 37.41 seconds west longitude, NAD83 - U.S.G.S Quad: South
Lake Tahoe, Calif. - Nev.
RANGE IN CHARACTERISTICS:
Soil moisture: usually moist between depths of about 12 and 35 inches but is dry in all parts from
late June until mid-October
Soil temperature: 5 to 8 degrees C.
Control section:
Reaction: Strongly acid to Slightly acid.
Rock fragments: 1 to 15 percent, with 2 to 15 percent gravel, 0 to 10 percent cobbles and
paracobbles, individual horizons have more fragments.
Clay content: averages 0 to 7 percent clay
Mineralogy: mixed
A horizon(s):
Hue: 10YR
Value: 4 or 5 dry; 3 or 4 moist
Chroma: 3 or 4 dry; 2 or 3 moist
Organic matter: 1 to 5 percent
Texture (less than 2 mm): Loamy coarse sand or loamy sand
Clay content: 0 to 5 percent
Content of rock fragments: 1 to 30 percent
0 to 5 percent cobbles
1 to 10 percent gravel
Bw horizons:
Hue: 10YR
Value: 4 through 6 dry; 4 or 5 moist
Chroma: 3 or 4 dry; 3 or 4 moist
Organic matter: 0.25 to 1.25 percent
Texture (less than 2 mm): Loamy coarse sand or Loamy sand
Clay content: 0 to 7 percent
Content of rock fragments: 1 to 30 percent
0 to 10 percent cobbles
1 to 10 percent gravel
C horizon where present:
Hue: 10YR
Value: 4 through 6 dry; 4 or 5 moist
Chroma: 3 or 4 dry; 3 or 4 moist
Organic matter: 0.25 to 1 percent
Texture (less than 2 mm): Loamy coarse sand
Clay content: 1 to 5 percent
Content of rock fragments: 10 to 55 percent
COMPETING SERIES: These are the Cagwin and Cassenai soils. Cagwin is 20 to 40 inches to
soft bedrock. Cassenai is formed in colluvium on mountainslopes and has 15 to 35 percent
fragments in the control section.
GEOGRAPHIC SETTING: Christopher soils are on glacial outwash terraces. Slopes are 0 to
30 percent. These soils formed in colluvium, alluvium and glacial outwash weathered from
granodiorite. Elevation is 1895 to 2090 meters. The climate is subhumid with cool dry summers
and cold moist winters. Mean annual precipitation is 530 to 990 millimeters. The mean annual
temperature is 5 to 8 degrees C. Frost free season is 40 to 90 days.
GEOGRAPHICALLY ASSOCIATED SOILS: These are the Gefo, Jabu, Marla and Oneidas
soils. The Gefo soils have an umbric epipedon. Jabu and Oneidas soils have argillic horizons.
Marla is somewhat poorly drained.
DRAINAGE AND PERMEABILITY: Somewhat excessively drained; very low to medium
runoff; rapid permeability. The soils are not flooded.
USE AND VEGETATION: This soil is used for wildflife, recreation, timber, and urban
development. Vegetation is predominantly Jeffrey pine with an understory of green leaf
manzanita, antelope bitter brush, mountain whitethorn, mahala mat, mules ear and lupin spp.
DISTRIBUTION AND EXTENT: These soils are of minor extent in the Tahoe Basin of
California and Nevada in MLRA 22A.
MLRA SOIL SURVEY REGIONAL OFFICE (MO) RESPONSIBLE: Davis, California
SERIES ESTABLISHED: El Dorado County, (Tahoe Basin area), California. The Source of
the name is from a local lake.
REMARKS:
Diagnostic horizons and features recognized in this pedon are:
Particle Size Control Section for this pedon: 28 to 103 cm, portions of the Bw1, Bw2, and Bw3
National Cooperative Soil Survey
U.S.
Appendix G: Streamkeepers Monitoring Report
The South Lake Tahoe Streamkeepers
~ A Citizen Monitoring Group ~
Draft Summer 2012 Monitoring Report
January 2013
Prepared by the Tahoe Resource Conservation District in concert with the Community
Watershed Partnership Program
Table of Contents
I. Introduction ................................................................................................
II. Monitoring Goals and Objectives ...............................................................
III. Summer 2012 Monitoring...........................................................................
IV. Methodology and Materials ........................................................................
V. Data Presentation and Discussion ...............................................................
VI. Conclusion .................................................................................................
VII. Works Cited ...............................................................................................
VIII. Appendix....................................................................................................
Introduction
The South Lake Tahoe Streamkeepers Citizen Monitoring Group (Streamkeepers) are a
volunteer based citizen monitoring group that was created in partnership with the Tahoe
Resource Conservation District (Tahoe RCD) and California Trout (CalTrout) in the Spring of
2012. Streamkeepers was developed in attempt to better educate and engage community
members of South Lake Tahoe in the monitoring of their local watersheds through a series of
annually reoccurring volunteer monitoring events.
The purpose of this initial report is to provide a complete program description of The South
Lake Tahoe Streamkeepers and to present data collected during the 2012 Streamkeepers
monitoring events.
Program Description
The mission of the Streamkeepers Monitoring Group is to promote community stewardship
through education, collaboration, and action.
Streamkeepers is designed to encourage community members throughout the South Lake
Tahoe region to become active environmental stewards. By providing volunteer experiences
that are both educational and action oriented, the Streamkeepers seek to develop an ever-
expanding base of citizen volunteers that can reliably provide watershed information to the
Tahoe RCD and CalTrout as well as function autonomously as community stewards in their
everyday life. The functional benefits of all Streamkeepers volunteer opportunities are
designed to be two fold; to educate community members regarding current ecological
conditions and resource issues in the community; and to capture sound scientific information
that can be used to further the understanding of local ecosystems. In creating the educational
components of volunteer opportunities, the Tahoe RCD compiles and organizes resources that
are designed to provide volunteers with a sound cultural, scientific, and ecological
understanding of the South Lake Tahoe watersheds.
The Streamkeepers program is also designed to assist partner organizations in the collection of
stream habitat and water quality data. In the situation where partner organizations have the
desire to capture information that is out of the capacity of their organization to do so,
Streamkeepers seeks to identify those opportunities and provide volunteer assistance where
appropriate. In utilizing the existing partnerships of the Tahoe RCD and CalTrout,
Streamkeepers has the potential to be of a high degree of utility to those organizations with
identified opportunities.
Streamkeepers was partially created to extend the efforts and capture engaged volunteers
created through the event Snapshot Day. The long-standing annual water quality monitoring
event occurs every spring and has historically recruited hundreds of volunteers, but rarely
does participation continue through the summer and fall. It is speculated that participation
slows over the summer as large scale monitoring events occur less frequently and small scale
events are often less publicized. Acknowledging this decline in summer participation,
Streamkeepers was created with the intention of retaining volunteer interest in watershed
monitoring created through the efforts of Snapshot Day. It is standard procedure of
Streamkeepers to contact all previous Snapshot Day volunteers that have expressed interest in
watershed monitoring prior to any planned Streemkeepers event.
Monitoring Goals and Objectives
The primary goals of the Streamkeepers Citizen Monitoring Group are as follows:
To better understand the physical and biological conditions of the watersheds in the
South Lake Tahoe region
To educate and empower citizens to become watershed stewards
To aid watershed managers in the identification of restoration and/or conservation
opportunities
The primary objectives of the Streamkeepers Citizen Monitoring Group are as follows:
Produce an annual Streamkeepers Monitoring report to share with the public on the
Tahoe RCD website
Identify funding opportunities and secure long term financial support for citizen-based
monitoring actions in the Lake Tahoe Basin
Create targeted monitoring inquiries that can provide better understanding of
watershed condition in relation to management practice, land use, and other natural
occurrences within the watersheds of the South Lake Tahoe region
Educate community members regarding watershed process and function in attempt to
increase community-based stewardship action
Identify existing organizational needs for watershed monitoring and incorporate
interagency efforts into Streakeepers events
Summer 2012 Monitoring
Tahoe RCD and CalTrout collaborated on three separate monitoring events during the field
season of 2012. The first event was the 13th annual Lake Tahoe Snapshot Day held basin-wide
on May 12th. Snapshot day is an annual volunteer-based monitoring event in early spring that
utilizes volunteer groups to measure Lake Tahoe tributaries for water quality and habitat
integrity. The second and third collaborations were comprised of two separate Streamkeepers
events on August 22nd and August 25th, respectively, which sought to measure stream
conditions as well as map and treat invasive weeds. Physical and biological indicators related
to stream bank stability, bed sediment, macroinvertebrates, and water quality were collected in
three South Lake Tahoe locations during these events.
All Streamkeeper data collected in the summer of 2012 occurred at selected locations within
the urban corridor of the Trout Creek Watershed. Although both Trout Creek and the Upper
Truckee River were originally slated for monitoring during the 2012 summer field season, due
to the lack of in-stream flow associated with the mild winter of 2012, only Trout Creek was
sampled. The selection of Trout Creek was based upon the identification of The Trout Creek
Watershed as a CWP focus areas for the summer 2012 field season. Community members in
this sub-watershed were specifically targeted for participation in stewardship events through
Tahoe RCD’s network of social media, newsletter releases, press releases, and member lists. A
complete description of the CWP program and focus areas can be accessed through the Tahoe
RCD website (tahoercd.org).
A total of 11 participants appeared for the August 25th event. Volunteers were recruited by
sending an invitation email to all CalTrout and Tahoe RCD volunteers, by posting an event
flier on the Tahoe RCD website, and by posting fliers around the City of South Lake Tahoe. A
group picture off all the participants from the August 25th event can be seen below in Figure 1.
South Lake Tahoe Streamkeepers 2012
Figure 1. South Lake Tahoe Streamkeepers Participants - 2012.
Watershed Background
The Trout Creek Watershed is the second largest watershed in the Lake Tahoe Basin (it occupies
13 percent of the total land area draining to Lake Tahoe) and is located primarily in the Eastern
portion of El Dorado County and partially in the Western portion of Douglas County. The area
of the watershed is 41.3 square miles and contains the main hydrologic features of Saxton
Creek, Cold Creek, Trout Creek, and Heavenly Valley Creek. An image of the Trout Creek
Watershed is presented below in Figure 2.
Figure 2. Trout Creek Watershed located in the southern portion of the Lake Tahoe Basin, California.
Trout Creek originates south of Freel Peak in the Carson Range of the Sierra Nevada mountain
range. It converges with Saxon Creek in Lake Valley, with Cold Creek and Heavenly Valley
Creek north of Pioneer Trail, and then enters the Upper Truckee Meadows before finally
draining into Lake Tahoe (Rowe). The main channel length of Trout Creek is approximately 19.5
km long.
The watershed includes the residential areas of Al Tahoe, the Sierra Tract, Black Bartt,
Montgomery Estates, Golden Bear, and Apalachee as well as the Montgomery Estates
Community Watershed Planning Area. The southern portion of the watershed is primarily
rural US Forest Service land, whereas the northern portion of the watershed consists of the
urbanized City of South Lake Tahoe.
Trout creek was once one of the most productive fisheries in the Tahoe Basin and held special
significance for the Washoe tribe. Trout Creek (mathOcahuwO’tha in Washoe, meaning “White
Fish river”) was an important fall camp for the tribe. Due to a growing population in Lake
Valley and continued disturbances and degradation of fish populations and habitat, the tribe
discontinued use of the Trout and Cold Creek area in the 1940’s.
Small scale logging began in the Trout Creek area in 1859 and within the Tahoe Basin in the
early 1860’s to supply lumber for the silver mines in Virginia City, Nevada and the surrounding
areas. Logging impacts within the Trout Creek watershed included 13 miles of railroad, 16 miles
of wagon haul roads, two miles of “V” flume, and 28 logging camps. It is noted that the highest
density and most severe erosion in the South Shore occurred along Trout and Saxon Creeks.
After the decline of the logging industry in Lake Valley, extensive grazing of cattle and sheep
began to take place in the headwaters and riparian areas of the watershed. A ditch system and a
series of small dams were developed along the tributaries on Trout and Cold creeks to water the
meadows during dry summer months. By today’s standards, impacts from sheep and cattle in
the watershed would likely be excessive and unnecessary (Lindström, 2000).
Today, the Trout Creek Watershed is occupied by roughly 3160 single family and multiple
family dwellings, and is commonly used by residents and visitors alike for swimming, fishing,
biking, and dog walking. The creek is closely bordered by urban development in multiple areas
including The Lake Tahoe Community College as well as the communities of Montgomery
Estates, the Sierra Tract, and Al Tahoe. Within the southern portion of the watershed where
Trout Creek winds through the urbanized corridor in The Upper Truckee Meadows, there are
currently three separate roads that intersect and cross Trout Creek; Highway 50, Pioneer Trail,
and Martin Ave. It is important to note, that where areas adjacent to the watershed are
urbanized and contain a high density of residents, user trails along-side and leading up to the
creek occur in a higher density and are more traveled upon than those in less developed areas
of the watershed.
In accordance with the LRWQCB Basin Plan, Trout Creek is listed with the following beneficial
uses: SPWN, MIGR, WILD, COLD, COMM, REC-1, REC-2, GWR, AGR, MUN. According to
LRWQCB beneficial uses, a body of water is afforded unique management conditions and
provisions. A full description of each beneficial use can be found in table 5 in the appendix.
Monitoring Locations
The Streamkeeper monitoring events at Trout Creek focused primarily on the lower
sections of the watershed where Trout Creek flows through the extensive urban Stream
Environment Zone (SEZ), merges with the Upper Truckee River in one of the largest
meadow systems in the Lake Tahoe Basin (the Upper Truckee Marsh), before it finally
reaches Lake Tahoe at Cove East. The selection of this monitoring area was based upon
the severity of historic and current environmental impacts within the meadow system;
impacts from upstream development and land management actions; proximity to
volunteers in the City of South Lake Tahoe; as well as ease of access to monitoring sites.
Three monitoring reaches, or linear segments along the creek, were selected within the
monitoring area for the Streamkeepers monitoring events. The first reach, identified as
TC-BB1, is located upstream from the confluence of Trout Creek and the Upper Truckee
River and below the intersection of Highway 50 at the bridge; the second reach,
identified as TC-AB1, is roughly 930 feet upstream of the Highway 50 bridge; and the
third reach, identified as TC-AB2 is located just downstream of the confluence of
Heavenly Valley Creek and Trout Creek roughly 470 feet below the intersection of
Trout Creek and Martin Avenue in South Lake Tahoe, California. Figure 3 below
provides a display of the approximate locations of the three stream reaches for the
Streamkeepers monitoring events in relation to Highway 50, The Upper Truckee River,
Lake Tahoe Community College and Lake Tahoe.
Figure 3. Upstream and downstream locations of three Stream Condition Survey Sites located on Trout
Creek, South Lake Tahoe, California.
The specific geographic location of each reach can found in Table 4 of the Appendix. It
is important to note, that all geographic coordinates are taken in the NAD 1983
coordinate system.
Methodology and Materials
Collection methodologies for all Streamkeepers monitoring data were created based
upon protocols established by the California State Water Resources Control Board
(SWRCB) through the Surface Water Ambient Monitoring Program (SWAMP).
Although SWAMP monitoring protocols were not used directly, simplified versions
that effectively capture the same information, but to a less technical extent, were created
for ease of volunteer use and comprehension. Monitoring procedures utilized by the
Streamkeepers include water quality sampling, benthic macroinvertibrate sampling,
stream bank stability assessment, stream bed substrate sampling, and invasive weed
mapping. The physical and chemical measurements that comprise the individual
components of water quality include Ph, water temperature, Dissolved Oxygen (DO),
electrical conductivity, turbidity, and in select locations, fecal coliform bacteria. Blank
versions of data collection forms can be found in the appendix of this document.
Monitoring equipment utilized during Streamkeepers events consist of an assortment of
instruments and kits. The measurement of water quality parameters, as mentioned
above, is captured through the use of two instruments and one kit: a handheld Hannah
pH meter with built-in thermometer (0.02 unit and .10 C resolution); a hand-held
Oakton Total Dissolved Solids (TDS) conductivity meter (10 µS/cm resolution); and a
Chemet DO kit (1 mg/L resolution below 6 mg/L and 2 mg/L resolution above 6
mg/L). All monitoring instruments and kits are directly under possession by the Tahoe
RCD and are calibrated prior to the beginning of each monitoring season to assure the
scientifically sound collection of data.
Benthic macroinvertebrate samples were taken, but due to a suspected low number of
individuals found, and due to funding shortages needed to send samples to a
laboratory to process the samples, no laboratory analysis was conducted for this
component. In order to completely process and assign a Benthic Macroinvertibrate
(BMI) score, laboratory analysis of macroinvertebrates requires a minimum of 500
sampled organisms. In both reaches sampled, it was generally deduced by team leaders
that the minimum number of 500 organisms was not exceeded, and therefore the
samples were not submitted for further analysis
Prior to the August 25th volunteer event, selected group leaders were required to attend
a special training event in order to increase their capacity as educators and event
facilitators. It is the understanding of CalTrout and the Tahoe RCD, that with previous
experience and understanding of sampling methodologies, team leaders are better
suited to aid untrained volunteers and field any inquiries that may arise. Team leader
training for the August 25th Streamkeepers event was led by Kim Gorman, Tahoe RCD
Watershed Coordinator and Field Biologist, on August 22nd along Trout Creek in the
Upper Truckee Meadows near the Lake Tahoe Community College (see figure 3 for
general geographic location). During the training event, team leaders were introduced
to field protocols that address qualitative visual assessment, photo-documentation,
water quality measurement, and water sampling. As a desired key element of these
trainings, team leaders become confidently familiar with Streamkeepers methodologies
and equipment though the direct application and use thereof.
Water Quality Standards and Thresholds
In accordance with the Environmental Protection Agency (EPA) Clean Water Act
(CWA) of 1972, the third chapter of the Lahontan Regional Water Quality Control Board
(LRWQCB) Basin Plan establishes water quality standards for the entire Lahontan
Basin, with more stringent requirements for the Lake Tahoe Basin hydrologic unit
(which occurs entirely within the Lahontan Basin). Unique water quality standards
exist for Trout Creek for TDS, Cl, SO4, B, N, P, and Fe but not for the remainder of
parameters listed in Table 1 below. For those standards that are not directly provided
for Trout Creek, the standards for the Lake Tahoe Hydrologic Unit are used in place.
Table 1. Water quality standards for surface waters of Trout Creek, as established by the LRWQCB.
Parameter Standard
TDS 50/60
Cl .15/.20
SO4 -
B -
N .19/-
P .015/-
Fe .03/-
DO
30 day Mean no less than 6.5 and one day minimum of 4.0 mg/L for Lahontan waters designated as “cold
freshwater habitat” (CA)
Turbidity (NTU)
Turbidity shall not exceed 3 Nephelometric Turbidity Units (NTU). In addition, turbidity shall not exceed 1 NTU in shallow waters not directly
influenced by stream discharges
pH 7 - 8.4
Temperature Shall not exceed 15° C
Conductivity
the mean annual electrical conductivity shall not exceed 95 umhos/cm at (50EC at any location in the
Lake)
Data Presentation and Discussion
Figures 4 - 6 contain the relative percentage of substrate class, bank stability, and bank
cover in a side-by-side display to provide a means for comparison among the three
surveyed reaches.
For substrate class, percentages ranged between 23% and 46% for the silt, clay, or mud
class, between 54% and 68% for the sand class; and between 0% and 12% for the gravel
class. TC-BB1 was composed of 23% silt, clay, or mud; 68% sand; and 10% gravel. TC-
AB1 was composed of 46 % silt, clay, or mud; 54% sand; and 0% gravel. TC-AB2 was
composed of 23% silt, clay, or mud; 65 percent sand; and 12 % gravel.
Figure 4. Substrate class by relative percentage for transects TC-BB1, TC-AB1, and TC-AB2
For bank stability, percentages ranged between 9% and 72% for the stable classification;
9% and 63% for the potential to erode classification; and from 9% to 59% for the eroding
classification. The banks of TC-BB1 were rated as 36% stable, 9% with potential to
erode, and 55% eroding. The banks of TC-AB1 were rated as 64% stable, 27% with
potential to erode, and 9% eroding. The banks of TC-AB2 we rated as 59% stable, 32%
with potential to erode, and 9% eroding.
22
46
23
68
54
65
10 0
12
0%
10%
20%
30%
40%
50%
60%
70%
80%
90%
100%
TC-BB1 TC-AB1 TC-AB2
Substrate Class by Percentage
gravel
sand
silt, clay, mud
Figure 5. Bank stability by relative percentage for transects TC-BB1, TC-AB1, and TC-AB2
For bank cover, percentages ranged between 0% and 4% for rock, 63% and 93% for
vegetated, 0% and 5% for wood, and 5% to 32% for bare. The banks of TC-BB1 were
covered with 4% rock, 91% vegetation, and 5% were bare. The banks of TC-AB1 were
covered with 63% vegetation, 5% wood, and 32% were bare. The banks of TC-AB2 were
composed of 82% vegetation and 18% were bare.
Figure 6. Bank cover by relative percentage for transects TC-BB1, TC-AB1, and TC-AB2
Tables 1 and Table 2 presented below represent the water quality measurements taken
at transect TC-BB1 and TC-AB2 respectively. Water quality measurements for TC-AB1
36
64 59
9
27 32 55
9 9
0%
10%
20%
30%
40%
50%
60%
70%
80%
90%
100%
TC-BB1 TC-AB1 TC-AB2
Bank Stability by Percentage
Eroding
Potential to Erode
Stable
4 0 0
91
63
82
0
5
0
5
32 18
0%
10%
20%
30%
40%
50%
60%
70%
80%
90%
100%
TC-BB1 TC-AB1 TC-AB2
Bank Cover by Percentage
bare
wood
vegitated
rock
were not taken during team leader training session at transect TC-AB1, and therefore no
data is available. As the proper device for measuring conductivity was unavailable
during both Streamkeepers events, no data was collected in regard to that indicator, but
the value of the indicator is still upheld by the group.
Table 2. Water quality measurements taken at transect TC-AB1
Parameters Units 1st Result
2nd
Result
Avg.
Result
Temperature 0C 14 14 14
DO mg/L 10 10 10
TDS µS/cm 60 60 60
pH - 8.2 7.7 8
Conductivity µS/cm
Table 3. Water quality measurements taken at transect TC-AB2
Parameters Units 1st Result
2nd
Result
Avg.
Result
Temperature 0C 13.9 13.4 13.65
DO mg/L 9 9 9
TDS µS/cm 70 70 70
pH - 7.5 7.4 7.45
Conductivity µS/cm
Conclusion
The field season of 2012 represents the initial set of Streamkeepers data within the Upper
Truckee Meadows along Trout Creek and proves infeasible to track any changes in physical
condition within the watershed. However, despite the pitfall of not providing information on
temporal condition change, this set of data functions to provide baseline information and acts
as a screening level effort that can provide information that does not require a precise,
technical level of analysis. From the information gathered in this initial year of the program,
Streamkeepers can prepare future monitoring events with more focus and question-driven
approach. For example, in review of the differences
It may be in the best interest of the Streemkeepers and Tahoe RCD to create a platform for
volunteer opportunities that requires less professional guidance. Although the professional
oversight necessary to organize and guide volunteers is not organizationally overbearing,
there may be a higher chance of developing long term community driven stewardship if there
were additional outlets for volunteering that were not specifically confined to monitoring
events. In addition to gathering water quality and stream habitat data, an auxiliary purpose of
the Streamkeeper events is to further develop the Tahoe RCD’s ability to produce community
supported events.
Works Cited
Lindström, Susan. "Chapter Two: A Contextual Overview of Human Land Use and Environmental
Conditions." Lake Tahoe Watershed Assesment. Vol. 1. Berkely: Pacific Southwest Research Station,
2000. N. pag. Print.
Rowe, Timothy G., and Kip K. Allender. Rep. no. 00-4001. USGS, n.d. Web.
Appendix
Table 4. Geographic location (captured using NAD 1983) for the upstream and downstream boundaries of the
bioassement reaches monitored in 2012 by the Streamkeepers Monitoring Group.
Name of Reach
Downstream Latitude
Downstream Longitude
Upstream Latitude
Upstream Longitude
TC-BB1 38.93273 -119.98368 38.93254 -119.98212
TC-AB1 38.93013 -119.97643 38.92945 -119.97631
TC-AB2 38.92178 119.97266 38.921 -119.97249
Table 5. Definition of Beneficial Uses
Abbreviation Definition
SPN
Spawning, Reproduction, and Development. Beneficial uses of waters that support high quality aquatic habitat necessary for reproduction and early development of fish and wildlife.
MIGR
Migration of Aquatic Organisms. Beneficial uses of waters that support habitats necessary for migration, acclimatization between fresh and salt water, or temporary activities by aquatic organisms, such as anadromous fish.
WILD
Wildlife Habitat. Beneficial uses of waters that support wildlife habitats including, but not limited to, the preservation and enhancement of vegetation and prey species used by wildlife, such as waterfowl.
COLD
Cold Freshwater Habitat. Beneficial uses of waters that support cold water ecosystems including, but not limited to, preservation and enhancement of aquatic habitats, vegetation, fish, and wildlife, including invertebrates.
COMM
Commercial and Sportfishing. Beneficial uses of waters used for commercial or recreational collection of fish or other organisms including, but not limited to, uses involving organisms intended for human consumption.
REC-1
Water Contact Recreation. Beneficial uses of waters used for recreational activities involving body contact with water where ingestion of water is reasonably possible. These uses include, but are not limited to, swimming, wading, water-skiing, skin and scuba diving, surfing, white water activities, fishing, and use of natural hot springs.
REC-2
Noncontact Water Recreation. Beneficial uses of waters used for recreational activities involving proximity to water, but not normally involving body contact with water where ingestion of water is reasonably possible. These uses include, but are not limited to, picnicking, sunbathing, hiking, beachcombing, camping, boating, tidepool and marine life study, hunting, sightseeing, and aesthetic enjoyment in conjunction with the above activities.
GWR
Ground Water Recharge. Beneficial uses of waters used for natural or artificial recharge of ground water for purposes of future extraction, maintenance of water quality, or halting of saltwater intrusion into freshwater aquifers.
AGR
Agricultural Supply. Beneficial uses of waters used for farming, horticulture, or ranching, including, but not limited to, irrigation, stock watering, and support of vegetation for range grazing.
MUN
Municipal and Domestic Supply. Beneficial uses of waters used for community, military, or individual water supply systems including, but not limited to, drinking water supply.
Appendix H: Invasive Weeds Mapping and Removal Data